• 한국산림과학회지
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• 제103권1호
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• pp.1-11
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• 2014

본 연구는 계방산 온대북부 낙엽활엽수림에서 하층식생(관목층과 초본층)의 식생조성 변화를 구명하였다. 조사지에 출현하는 식물은 56과 93속 124종 17변종 3품종 2아종 1미분류군으로 총 146분류군이 조사되었으며, 종면적 곡선에서 초본층과 관목층의 종수는 시간이 경과함에 따라 감소하는 것으로 나타났다. Mantel-test 분석 결과, 상층의 기저면적은 하층의 변화에 영향을 주는 인자 중 하나로 분석되었다(p < 0.0001). 평균중요치는 관목층에서 생강나무(21.585%), 철쭉(19.774%)이 우점하는 것으로 분석되었으며, 초본층에서는 조릿대(14.082%)와 생강나무(7.921%)가 우점하는 것으로 나타났다. 관목층의 NMS 배열 결과, 높은 연관성을 가지는 종은 시간이 경과함에 따라 감소하는 것으로 분석되었으며, 상층의 기저면적 증가에 따라 반응하는 종이 다른 것으로 분석되었다. 초본층 조사구의 NMS 배열 결과, 관목층의 철쭉과 진달래가 지속적으로 영향을 미치는 것으로 분석되었다. 그리고 MRPP-test에 대한 식생조성의 변화 결과, 관목층은 5년 그리고 10년에 따른 식생조성의 변화가 유의차가 없는 것으로 분석되었다. 하지만 초본층은 5년 그리고 10년에 따른 식생조성의 변화가 유의성 있게 분석되어, 하층식생 중 초본층의 종조성은 관목층보다 종조성의 변화가 큰 것으로 나타났다.

• Journal of Plant Biology
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• 제15권1호
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• pp.33-41
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• 1972

Nine shrub layer communities under two relatively well conserved natural summer green forests in the central region of Korean Peninsula were studied for the pattern of stem distribution in terms of Greig-Smith's multiple split-plot experiment and for the association between the population of the two main species in terms of Kershaw's covariance analysis respectively. Four contiguous belt transects, $4{\times}64m size with 1{\times}1m$ basic unit, were set in each shrub layer communities. Significant primary clumps with $1{\times}1m or 1{\times}2m$ dimension wer observed consistently throughout the nine study sites. The primary clumps themselves were significantly distributed either regularly or at random. The association between the two principal species of each shrub layer is highly significantly either positive or negative in $1{\times}1m or 1{\times}2m$ dimension. As the plot size increases from $1{\times}1m to 8{\times}8m$ the associational trends were changed from negative to positive direction in one forests. But the change from positive to negative direction and the consistent negative association were also observed from the other forest. All of the association trends were observed only from $1{\times}1m to 4{\times}4m$ dimension. These results are suggestive that the distributional pattern of the shrub layer species under the summer green forest is simple mosaic fashioned with $1{\times}1m or 1{\times}2m$ dimension. The rest of the principal species are located in that matrix. The simple mosaic pattern of two principal species are located in that matrix. The simple mosaic pattern of two principal species seems to be controlled by change in micro-environmental pattern. Differences between the primary random group and clumped group among sites also suggest that competition exists for light or/and soil between primary clumped groups.

• 한국환경복원기술학회지
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• 제15권2호
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• pp.77-84
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• 2012

This study suggested the planting model of Zelkova serrata communities in the areas with the warmth index of both 80~100 and $100{\sim}120^{\circ}C{\cdot}month$. Warmth index was calculated with 449 weather points using inverse distance weighted interpolation method. The planting species were selected by correlation analysis between Z. serrata and each species of four or more frequency among the 36 relev$\acute{e}$ surveyed for this study. The result of this study is summarized as follows : Warmth index of Z. serrata communities was among $74{\sim}118^{\circ}C{\cdot}month$. Results of the correlation analysis between Z. serrata and each species observed that the Z. serrata belongs to the tree layer with warmth index of 80~100 and $100{\sim}120^{\circ}C{\cdot}month$. On the other hand, the species of Carpinus laxiflora, Quercus serrata, Prunus sargentii and Platycarya strobilacea appeared only in the tree layer with warmth index of $80{\sim}100^{\circ}C{\cdot}month$. Z. serrata and Styrax japonica appeared in the subtree layer with the warmth index of 80~100 and $100{\sim}120^{\circ}C{\cdot}month$, while Acer pseudosieboldianum, Lindera erythrocarpa, Acer mono, Quercus serrata, etc. appeared in the subtree layer with the warmth index of $80{\sim}100^{\circ}C{\cdot}month$. Z. serrata, Ligustrum obtusifolium, Lindera obtusiloba, Callicarpa japonica and Zanthoxylum schinifolium all appeared in the shrub layer with the warmth index of 80~100 and $100{\sim}120^{\circ}C{\cdot}month$. Lindera erythrocarpa, Orixa japonica, Staphylea bumalda, Akebia quinata and Sorbus alnifolia appeared in the shrub layer with the warmth index of $80{\sim}100^{\circ}C{\cdot}month$ and Styrax japonica and Stephanandra incisa appeared in the shrub layer with the warmth index of $100{\sim}120^{\circ}C{\cdot}month$, The numbers of each species planted in a $100m^2$ area of the Z. serrata community were suggested as follows : five in tree layer, five in subtree layer and nine in shrub layer. The average area of canopy are suggested to be about $86m^2$ for tree layer, $34m^2$ for subtree layer and $34m^2$ for shrub layer.

• 환경영향평가
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• 제20권2호
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• pp.151-162
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• 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.

• 한국환경복원기술학회지
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• 제13권2호
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• pp.80-94
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• 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.

• 한국조경학회지
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• 제38권3호
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• pp.107-114
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• 2010

본 연구는 한국 온대중부지역 소나무림 군락식재 모델을 제시하기 위해 충청남도 당진군 일대 소나무림을 대상으로 다양한 경급의 소나무림을 조사하였다. 유령림부터 장령림까지 총 $10{\times}10m(100m^2)$의 방형구 92개소를 설치하고, 출현개체별 규격을 모두 조사하였으며, 개체간 생육거리 분석을 위해 44개 조사구에 대해서는 1/100 scale로 교목층과 아교목층 수목의 위치를 조사하였다. 분석결과, 모든 조사구의 교목층은 양호하게 발달해 있었으나, 아교목층의 흉고단면적이 교목층의 10%에 미치지 못하고 있었으며, 관목층의 경우 일정한 피복율을 보이지 않고 조사구마다 매우 다양하였다. 이에 소나무 군락식재는 교목층과 관목층의 구조로 조성하는 것이 바람직한 것으로 판단되었으며, 관목층의 경우에는 특정 경향이 없어 식재하려는 인접 지역의 소나무림을 별도로 조사하여 적용하는 것이 바람직한 것으로 판단되었다. 군락식재 모델을 위한 소나무 교목층 흉고직경급별 단위면적당 생육개체수 및 단위면적당 생육개체수와 생육수목간 최단거리와의 회귀식은 높은 설명력을 보였다.

• 농업생명과학연구
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• 제46권6호
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• pp.33-41
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• 2012

본 연구는 덕유산, 계방산의 가문비나무 군락의 보존을 위한 기초자료를 제시하기 위하여 종조성과 흉고직경급을 조사, 분석하였다. 두 조사지의 교목 아교목 관목층의 층위별 식생은 덕유산이 8, 20, 26종, 계방산이 12, 23, 33종으로 구성되어 있다. 층위별 중요치 분석 결과, 덕유산 교목층은 가문비나무, 사스래나무, 구상나무, 아교목층은 사스래나무, 신갈나무, 관목층은 조릿대가 중요치가 높았으며, 계방산의 교목층은 가문비나무, 사스래나무, 분비나무, 아교목층은 시닥나무, 부게꽃나무, 관목층은 미역줄나무의 중요치가 가장 높은 것으로 분석되었다. 조사구의 층위별 종다양도의 경우 교목층은 덕유산 0.779, 계방산 0.984, 아교목층은 덕유산 1.052, 게방산 1.161, 관목층은 덕유산 0.823, 계방산 1.304로 분석되었다. 흉고직경 분포에서는 덕유산지역의 가문비나무 개체군이 역J형의 유형이 나타나고 있어 당분간 가문비나무군락이 유지될 수 있을 것으로 판단된다.

• Journal of Forest and Environmental Science
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• 제32권1호
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• pp.10-19
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• 2016

This study was carried out in the Boin and Miryousef regions in Baneh of Kordestan province, west of Iran. Both areas were divided into two parts including protected and unprotected areas. In each area, 20 $1000-m^2$ circular plots were established following a selective method. Tree and shrub species were identified and the number of these species was counted in each sampling plot. The results indicated that 7 trees, 4 shrubs and 109 herbaceous species were found in the studied areas, 40 herbaceous, 7 tree and 3 shrub species were present in protected area, while unprotected area had 16 herbaceous and 3 tree species. The highest value of diversity indices belonged to protected areas in all vegetation layers. In tree layer, Quercus brantii had the greatest value of SIV, whereas the lowest value belonged to Pistacia atlantica. In shrub layer, the highest and lowest values of SIV belonged to Daphne mezereum and Cerasus microcarpa, respectively. Finally, in herbaceous layer, Luzula spicata had highest value of SIV, and lowest value was belonged to Galium sp.

• 한국환경복원기술학회지
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• 제22권4호
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• pp.47-64
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• 2019

The purpose of this study is to present the basic data for the management of National Park by surveying and analysing the change of vegetation of forest fire damaged area in Sogeumgang District, Gyeongju National Park. The covergae ratio, a number of species and dominant species changed overall in forest fire damaged area. The final result of the change is as follows. In case of coverage ratio in the shrub layer, Site 1 was 30%, 40% in Site 2, 50% in Site 3, 60% in Site 4 and 30% in Site 5. In the herb layer, Site 1 was 90%, 80% in Site 2, 90% in Site 3, 60% in Site 4 and 20% in Site 5. In case of the number of species in the shrub layer, Site 1 was 11 species, 8 species in Site 2, 6 species in Site 3, 10 species in Site 4, 7 species in Site 5, and in the herb layer, Site 1 was 22 species, 25 species in Site 2, 12 species in Site 3 and Site 4 each and 11 species in Site 5. In the dominant species, the shrub layer was Lespedeza maritima(Site 1, 2), Quercus serrata(Site 3), Quercus serrata and Lespedeza bicolor(Site 4) and Styrax japonicus(Site 5), the herb layer was Miscanthus sinensis var. purpurascens(Site 1, 3), Pteridium aquilinum var. latiusculum and Carex humilis var. nana(Site 2), Quercus serrata(Site 4) and Carex humilis var. nana andS tyrax japonicus(Site 5). The number of vascular plants was summarized as 91 taxa including 35 families, 69 genera, 78 species, 2 subspecies, 10 varieties and 1 form.

• 한국산림과학회지
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• 제99권3호
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• pp.267-276
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• 2010

환경부 멸종위기 식물과 산림청 희귀식물로 지정된 왕제비꽃의 5개 지역 천연집단의 식생구조 및 입지환경을 조사한 결과 돌배나무-신나무-산뽕나무 우점군락(강원도 홍천군 내면), 신갈나무-물푸레나무-산뽕나무 우점군락(경기도 연인산), 층층나무-당단풍-산뽕나무 우점군락(경기도 유명산), 고로쇠나무-찰피나무(신갈나무)-고추나무 우점군락(경기도 대부산), 일본잎갈나무-고로쇠나무-물푸레나무 우점군락(충북 월악산)으로 조사되었으며, 자생지의 평균 산도는 pH 5.23, 전기전도도 0.30 ds/m, 유기물함량 12.6%, 전질소함량 0.68%, 유효인산 21.66 ppm 및 양이온치환용량 23.45 cmol(+)/kg로 나타났으며, 치환성양이온의 경우 $Ca^{2+}$ > $Mg^{2+}$ > $K^{2+}$순으로 감소하였다. 왕제비꽃은 둥굴레 및 이질풀과는 정의 상관관계가, 포아풀과는 부의 상관관계가 있는 것으로 나타났다. 목본층에서는 대부산 지역이, 초본층에서는 월악산 지역의 종다양성지수가 각각 0.9656, 1.3295로 가장 높았으며, 최대종다양도는 목본층의 경우 홍천군 내면 지역이 1.3010, 초본층의 경우 대부산 지역이 1.6435로 가장 높았다. 균재도의 경우 목본층은 일본잎갈나무 조림지인 월악산 지역(0.5330)을 제외하면 0.6185~0.8947 범위에, 초본층은 0.6984~0.8356 범위에 있었으며, 우점도는 목본층의 경우 월악산 지역(0.4670)을 제외하면 0.1053~0.3815, 초본층은 0.1644~0.3016의 범위에 있었다.