울릉도 섬잣나무림의 임분구조 및 동태

임종환 ( Im Jong Hwan ),김광택 ( Kim Gwang Taeg ),윤충원 ( Yun Chung Won ),신준환 ( Sin Jun Hwan ),배상원 ( Bae Sang Won ) 한국산림과학회 2004 한국산림과학회지 Vol.93 No.1

The information of natural process in forest development is utmost important for ecological forest management and conservation of biodiversity. This study was carried out to understand forest stand dynamics such as structure and productivity change of Pinus pawiflora forest in Ullengdo Island where we established a permanent plot in 1995 year. Forest stand characteristics were investigated in 1995 and 2003. The number of stems larger than 2 cm in DBH was 5,180 per hectare in 1995 and 4,780 in 2003, respectively. Basal area was increased from 60.17 m`/ha to 69.87 m`/ha. and annual biomass increment was 6.89 ton/ha. The annual number of recruited stems was 52.5 per hectare with the rate of recruitment of 1.14% in a year and the mortality was 102.5 stems/ha/year with the mortality rate of 2.13% in a year. Major cause of tree mortality was the suppression by canopy trees, and the mortality rate of individuals smaller than 10 cm in DBH was reached more than 95%. About 78.1% of the dead stems were standing death type. It was considered that the stand was in stem exclusion stage and still growing. And it was predicted that the Pinus panriflora forest would be replaced by Tsuga siebokiii forest if vast disturbance would not happen. It is needed that the researches on the characteristics of regeneration and long-term monitoring of the stand should be carried out for the conservation of the P. parutflora forest.

경상북도 신갈나무 성숙림에서 15% 군상잔존벌 이후 초기 하층식생 변화

( Zhang Ming ),김준수 ( Jun Soo Kim ),조용찬 ( Yong Chan Cho ),배사원 ( Sang Won Bae ),윤충원 ( Chung Weon Yun ),변봉규 ( Bong Kyu Byum ),배관호 ( Kwan Ho Bae ) 한국산림과학회 2013 한국산림과학회지 Vol.102 No.2

This study observed changes of understory vegetation to evaluate the role of forest aggregate after 15% aggregated retention harvest in mature oak forest (> 100 years) in Gyungsangbukdo Bonghwagun in 2010 and 2011. Spontaneous responses of understory vegetation cover (%), species richness, abundance of plant growth forms (herbaceous and woody plants), and overall attributes (by Ordination analysis) were estimated in aggregate area (0.15 and n=36) and clear cut area (0.85 and n=192) in experimental site and control site (1 and n=300). Based on ordination analysis, overall change of species composition in aggregated sites were relatively lower than in harvest area. Right after treatment, total cover of cutted area slightly decreased from 15.6% to 14.7%, and species richness increased from 14 species to 22 species. Cover and richness in the both of aggregate and control sites increased. In plant growth forms, 15% aggregate harvest revealed positive effects on the abundance (cover and richness) of herbaceous plants than woody group. After retention treatment, overall, edge effect likely played major component of vegetation changes in aggregate forest and in harvested area, mechanical damage from harvest operation and change of forest structure by clear cutting were critical. As pre-treatment data, which are rare in ecological studies in Korea, were critical for interpretation between patterns that may have arisen from spatial distributions in the original forest, our experimental design have higher opportunity for long term monitoring on the effect of forest aggregate and vegetation regeneration in clear cutted area.

계방산 가문비나무 및 전나무 임분의 산림식생유형분류와 정량적 분석

고승연 ( Seung Yeon Ko ),한상학 ( Sang Hak Han ),이원희 ( Won Hee Lee ),한심희 ( Sim Hee Han ),신학섭 ( Hak Sub Shin ),윤충원 ( Chung Weon Yun ) 한국환경생태학회 2014 한국환경생태학회지 Vol.28 No.2

본 연구는 계방산 가문비나무 및 전나무 임분의 산림식생유형분류와 정량적 분석을 위하여 Z-M 식물사회학적 방법으로 식생구조의 유형분류를 실시한 결과, 군락단위에서 가문비나무군락, 전나무군락으로 분류되었으며 가문비나무군락은 군단위에서 흰인가목군과 부게꽃나무군으로 세분되었으며, 전나무군락은 복장나무군과 생강나무군으로 세분되었다. 분류된 식생단위를 기준으로 중요치를 산출한 결과, 가문비나무는 식생단위 1과 2의 교목층에서 각각 30.73%, 20.25%로 비교적 높게 나타나 당분간 가문비나무의 우점이 계속될 것이라 판단되었다. 또한 종다양도를 분석한 결과 식생단위 4의 종다양도 지수는 0.6976으로 가장 낮았으며, 식생단위 2의 종다양도 지수는 1.1256으로 가장 높게 나타났다. 군락간의 유사도는 식생단위 1과 4, 2와 4가 각각 0.2880과 0.3626으로 낮게 나타났으며 식생단위 1과 2, 3과 4의 군락유사성은 각각 0.5411과 0.5041로 나타나, 군락 간 구성종의 차이가 크지 않은 군락으로 판단되었다. 종간연관에 대한 Chi-square matrix와 성좌표를 각각 분석한 결과, 크게 2개의 유형으로 나뉘어졌는데 Ⅰ유형의 식물 종들은 대부분 식물사회학적으로 분류된 가문비나무군락에서 주로 출현하는 식별종과 표징종이었으며, Ⅱ유형의 식물종은 전나무군락에서 주로 출현하는 식물종으로, 비교적 습한 곳에 나타나는 종들로 나뉘어졌다. 이러한 결과는 각 수종들이 선호하는 생육환경이 비슷한 종들끼리는 정의 상관이 인정되고, 선호하는 환경이 다른 종들끼리는 부의 상관을 보이는 것으로 판단된다. In this study, for the forest vegetation classification and the quantitative analysis of the Picea jezoensis and Abies hollophylla stand, the type classification of the vegetation structure was performed with Z-M phytosociological method, and as a result, it was classified into the Picea jenoensis community and the Abies holophylla community in the community unity. The Picea jezoensis community was subdivided into the Rosa koreana group and the Acer ukurunduense group in the group unity and the Abies holophylla community was subdivided into the Acer mandshuricum group and the Lindera obtusiloba group. In the results of estimating the importance value based on the classified vegetation unity, it was deemed that the dominance of the Picea jezoensis would be continued for a while as the importance value from the tree layers of vegetation unity 1 and 2 represented relatively high with 30.73% and 20.25%. In addition, in the results of analyzing the species diversity to estimate the maturity of the community, the species diversity index of the vegetation unity 4 was the lowest with 0.6976 and that of vegetation unity 2 was the highest with 1.1256. As in the similarity between the communities, the vegetation unit 1 and 4 and the vegetation unit 2 and 4 represented low with 0.2880 and 0.3626, respectively, and the similarity between the vegetation unit 1 and 2 and between 2 and 4 represented 0.5411 and 0.5041, respectively, it was deemed that they were the communities that the difference in the composition species between the communities was not big. In the results of analyzing the Chi-square matrix and the catalog of constellations for the interspecific, they were divided mainly into two types, and type 1 plant species were mostly differential species and the characteristic species, which appeared in the Picea jezoensis community classified phytosociologically, and type II plant species were mostly the species appearing in the Abies holophylla community growing in the relatively damp places. Such results is deemed that the positive (+) correlation is recognized among the species, of which growing environments are similar, and the negative (-) correlation .represents among the species, of which preferential environments are different.

강화도 마니산 산림식생의 군집구조 특성

신학섭 ( Hak Sub Shin ),신재권 ( Jae Kwon Shin ),김혜진 ( Hye Jin Kim ),한상학 ( Sang Hak Han ),이원희 ( Won Hee Lee ),윤충원 ( Chung Weon Yun ) 한국농림기상학회 2014 한국농림기상학회지 Vol.16 No.1

본 연구의 목적은 산림식생에 대한 기본 정보를 확인하고, 강화도 마니산에있는 산림의 효율적인 관리를 위한 산림식생의 계층구조와 관련된 식생학적 자료를 축적하는 데 있다. 샘플은 2010 년 8월에서 10월까지 수집된 32개소의 조사구에 대해 ZM학파의 식물사회학적 분석방법으로 식생군락을 구분하였고, 중요치 분석을 수행하였다. 식물사회학적 식생분석결과 산림식생은 여러 종들의 구분에 의해 2개 군락, 2개 군, 4개 소군으로 분류되었고, 복잡한 환경인자들에 의해 결정되어진 것으로 사료되는 식생유형은 총 5단위로 나타났다. 5개의 식생유형 중 식생단위1의 중요치는 소나무 54.31 (18.10%)로 나타났으며, 신갈나무 39.21 (13.07%), 식생단위2의 서어나무가 37.29 (12.43%), 신갈나무 89.43 (22.23%), 진달래 63,525 (14.43%)로 나타났다. 식생단위3에서 때죽나무의 중요치 53.97 (13.50%), 당단풍 33.60 (8.40%), 서어나무 26.48 (6.62%), 졸참나무 22.51 (5.64%)로 나타났으며, 식생단위4에서는 서어나무 47.70 (11.92%), 상수리나무 38.40 (9.60%)로 나타났고, 식생단위5의 쉬나무가 80.59 (20.14%), 아까시나무 35.00 (8.74%), 칡의 중요치가 28.63 (7.15%), 떡갈나무 28.20 (7.05)의 순으로 중요치가 나타났다. 이는 1997년 강화도의 기후와 산림생태계 현황(Lee, 1997)에서 온대중부림의 생태적 천이는 소나무에서 참나무류를 거쳐 서어나무류의 순서라는 학설이 거의 입증되었는데, 강화도 마니산의 산림식생은 천이발달의 중간단계로 보고한 바 있는데, 현재의 산림식생은 소나무군집, 신갈나무군집, 때죽나무군집, 서어나무군집, 쉬나무군집으로 분류되고, 각 식생단위에서 서어나무의 중요치가 높게 나타나는 것으로 미루어 인위적, 자연적 교란이 없는 한 서어나무로의 천이가 진행될 것으로 사료된다. The purpose of this study was to furnish basic information for forest community ecology and to accumulate vegetational datum related to hierarchy of forest community for the efficient management of forest vegetation in Mt. Mani. Samples were collected and analyzed by 32 releves from August to October in 2010 using phytosociological analysis methodology of Z-M school and importance value analysis. The results were summarized that the forest vegetation was classified into 5 units in total. Importance value at vegetation unit 1 indicated Pinus densiflora 54.31 (18.10%), Quercus mongolica 39.21 (13.07%), Carpinus coreana 37.29 (12.43%), at vegetation unit 2 Quercus mongolica 89.43 (22.23%), Rhododendron mucronulatum 57.75 (14.43%), Carpinus coreana 47.19(11.80%), at vegetation unit 3 Styrax japonica 53.97 (13.50%), Acer mono 33.60 (8.40%), Carpinus coreana 26.48 (6.62%), Quercus serrata 22.51 (5.64%), at vegetation unit 4 Carpinus coreana 47.70 (11.92%), Quercus acutissima 38.40 (9.60%) and at vegetation unit 5 Evodia daniellii 80.59 (20.14%), Robinia pseudoacacia 35.00 (8.74%), Pueraria thunbergiana 28.63 (7.15%), Quercus dentata 28.20 (7.05%) in the order, respectively.

충남 광역생태네트워크 자연녹지의 훼손 인자 및 원인에 관한 연구

이종문 ( Jong Mun Lee ),조용현 ( Yong Hyeon Cho ),김광동 ( Kwang Dong Kim ),이민우 ( Minwoo Lee ),김진기 ( Jinki Kim ),최정권 ( Jung Kwon Choi ),김원태 ( Won Tae Kim ),윤충원 ( Chung Weon Yun ),강희경 ( Hee Kyoung Kang ) 한국환경복원기술학회(구 한국환경복원녹화기술학회) 2015 한국환경복원기술학회지 Vol.18 No.6

This study aimed to classify damaged lands, to find what are the damage factors affecting the studied area, and to present a prescription in order to provide some benefit for the restoration of Regional Ecological Network at Chungnam province. Finally we classified damaged lands from 1st to 4th damaged lands according to relative intensity of damage. The main damage factors for the First Damage Lands were humus horizon, soil hardness and plant species richness. In the Second Damage Lands, those were soil hardness, plant species richness, number of plants and dominant plant species. In the Third Damage Lands, those were humus horizon, soil hardness, plant species richness, number of plants and dominant plant species. In the Fourth Damage Lands, those were humus horizon, organic matter, soil hardness, EC, T-N content, plant species richness, number of plants and dominant plant species. In every cases, the damage of soil and vegetation was originated due to development carried out by human being. The changes in soil condition were not big enough for it to affect plant growth, however, degradation of vegetation was still severe.