• 한국환경복원기술학회지
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• 제21권1호
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• pp.41-54
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• 2018

The purpose of this study was to present the fundamental data for conservation and management of wetland ecosystem by surveying and analysing the vascular plants distributed in major wetlands, Gyeongju National Park. The study sites were Tohamsan wetland, Amgok wetland and Namsan wetland. The numbers of vascular plants were summarized as 200 taxa including 70 families, 145 genera, 171 species, 2 subspecies, 23 varieties and 4 forms. The threatened species designated by Ministry of Environment was Utricularia yakusimensis, and the rare plants were 7 taxa including Utricularia yakusimensis, Drosera rotundifolia, Mosla japonica, Utricularia bifida, Pogonia japonica, Utricularia racemosa and Iris ensata var. spontanea. The Korean endemic plants were Lespedeza maritima and Weigela subsessilis. The specific plants by floristic region were 12 taxa including 3 taxa of grade V, 1 taxa of grade IV, 1 taxa of grade III, 2 taxa of grade II and 5 taxa of grade I. The plants with approval for delivering oversea were 9 taxa including Glycine soja, Saussurea pulchella, Habenaria linearifolia and so forth. The naturalized platns were 5 taxa including Rumex obtusifolius, Ambrosia artemisiifolia, Bidens frondosa, Erigeron annuus and Erigeron strigosus, the invasive alien plant was Ambrosia artemisiifolia.

• 한국환경복원기술학회지
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• 제10권3호
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• pp.52-59
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• 2007

This study was carried out to select proper species for early stage replantation in cutting-slope area of the Baekdu Range roadside. In the cutting-slope area and upper forest area of the cutting-slope area, sample plots of 46 were selected and their vegetations and environmental factors were investigated. We found total 90 species in the 46 plots. We found Festuca arundinacea in 27 plots of the 46 plots. We also found Lespedeza bicolor in 26 plots, Eragrostis curvula in 22 plots, Artemisia princeps var. orientalis in 19 plots, Erigeron annuus and Pinus densiflora in 15 plots, Lactuca indica var. laciniata in 14 plots, Miscanthus sinensis in 13 plots, Oenothera odorata, Commelina communis, and Humulus japonicus in 11 plots, Lespedeza cuneata in 10 plots, Salix koreensis and Salix hulteni in 9 plots, Festuca rubra, Youngia denticulata, Aster scaber, and Festuca arundinacea in 8 plots, Chenopodium album var. centrorubrum in 7 plots, Patrinia villosa and Erigeron canadensis in 6 plots, and Setaria viridis, Digitaria sanguinalis, and Dactylis glomerata in 5 plots.The dominancy of Festuca arundinacea, Eragrostis curvula, Lespedeza bicolor, Miscanthus sinensis, Pinus densiflora, Festuca arundinacea, Festuca rubra, Artemisia princeps var. orientalis, Erigeron annuus, Lespedeza cuneata, Dactylis glomerata, Salix koreensis, Alnus hirsuta, Pueraria thunbergiana, Medicago sativa, Lactuca indica var. laciniata, and Digitaria sanguinalis were 13.41% 11.87%, 4.88%, 4.56%, 3.38%, 2.29%, 2.14%, 2.14%, 1.99%, 1.95%, 1.54%, 1.47%, 1.44%, 1.37%, 1.15%, 1.13%, 1.07% in the roadside cutting-slope, respectively. The dominancy of Rhododendron mucronulatum, Lindera obtusiloba, Rhus trichocarpa, Quercus mongolica, Lespedeza bicolor, Rhododendron schlippenbachii, and Quercus serrata 22.15%, 13.36%, 13.14%, 12.03%, 11.74%, 11.20%, and 11.14% in shrub layer of the upper forest area, respectively. The species of Rhododendron mucronulatum, Lindera obtusiloba, Rhus trichocarpa, Rhododendron schlippenbachii, Zanthoxylum schinifolium, Weigela subsessilis, Stephanandra incisa, Rhamnus davurica, Ligustrum obtusifolium, Lindera erythrocarpa, Rosa multiflora, Rubus coreanus, Symplocos chinensis for. pilosa, Smilax china, Prunus sargentii, and Staphylea bumalda may be more helpful in stabilizing of the cutting-slope area and making harmony with the surrounding forest area.

• 한국잡초학회지
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• 제8권3호
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• pp.291-294
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• 1988

제주도(濟州道)의 목초지(牧草地)에 발생(發生)하는 하계잡초(夏季雜草)를 조사(調査)하여 얻어진 결과(結果)를 요약(要約)해 보면 다음과 같다. 1. 조사(調査)된 총(總) 잡초종수(雜草種數)는 44과(科) 136 여종(餘種)이었으며 국화과(菊花科) 29종(種), 벼과(科) 16종(種), 콩과(科) 14종(種), 장미과 13종(種), 마디풀과(科) 10 종순(種順)으로 많이 발생(發生)하였다. 2. 목초지(牧草地)에 우점(優占)하는 잡초종(雜草種)은 크로바, 늦고사리삼, 찔레꽃, 억새, 띠로 나타났다. 3. 잡초군락(雜草群落)은 쑥-늦고사리삼 군락(群落), 쑥-실망초/패랭이꽃 군락(群落) 및 쑥-싸리/억새 군락(群落)으로 대별(大別)되며 늦고사리삼, 실망초, 싸리, 억새가 식별종(識別種)으로 조사(調査) 되었다. 4. 발생빈도(發生頻度)로 본 우점초종(優占草種)은 쑥, 바늘엉겅퀴, 큰피막이, 찔레꽃, 오이풀, 산딸기, 양지꽃, 개망초, 질경이, 괭이밥, 쥐깨풀의 순(順)으로 많이 발생(發生)하였다.

• 한국자원식물학회지
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• 제20권4호
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• pp.353-361
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• 2007

본 조사는 2005년 5월 10일부터 2006년 12월 20일까지 전남 서남해권 목포시, 진도군, 영암군, 해남군, 신안군, 완도군, 무안군, 강진군 지역을 중심으로 이 지역에 분포하는 귀화식물상과 군락을 조사함으로서 귀화식물의 지리적, 서식지 특성별 분포실태에 따른 관리방안을 제시하였다. 조사된 귀화식물은 총 29과 84속 122종 8변종으로 총 130종류가 조사되었으며, 귀화률은 45%이고, 각 조사지역의 출현종수는 염암에서 103종, 목포에서 98종, 신안에서 97종으로서, 다른 지역보다 비교적 높게 나타났다. 총 30개 귀화식물군락으로 분류되었다. 8개 조사지역에서 공통으로 나타난 귀화식물군락은 아까시나무군락, 족제비싸리나무군락, 돌소리쟁이군락, 능수참새그령군락, 토끼풀군락, 호밀풀군락, 큰금계국군락, 큰김의털군락, 개보리군락, 털물참새피군락, 원추천인국군락, 다닥냉이군락, 개망초군락, 겹달맞이꽃군락, 개망초-망초군락, 쥐보리군락, 돼지풀군락, 들묵새군락, 코스모스군락, 노랑코스모스군락 등이며, 귀화식물의 분포특징은 서식지의 생태적 특성에 따라 6개 지역으로 구분하였다.

• 한국환경생태학회지
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• 제17권3호
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• pp.232-241
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• 2003

경기도의 축령산은 해발 879m로 광주산맥에 이어져 한국의 중부지역 북동부에 위치한다. 축령산 일대에는 한국의 특산식물 및 희귀 및 멸종위기식물 종이 흔히 분포하는 지역으로 널리 알려져 있다. 또한 북방계 식물과 남방계 식물의 한계선이 교차하는 식물지리학적으로 중요한 지역이다. 그러나 서울에서 거리가 가깝고 경관이 뛰어나 많은 관광객들의 탐방이 이어지고 있다. 대규모 관광객들의 지속적인 탐방은 등산로를 중심으로 주변 식생에 악영향을 미칠 수 있다. 따라서 인위적인 훼손에 직접적인 영향을 받는 등산로 주변의 잡초 군락에 대해 2001년 8월에서 2002년 9월까지 식물사회학적인 조사를 수행하여 등산로 주변에 형성된 군락을 유형화하고 그 환경조건을 분석하였다. 등산로 주변 잡초 군락은 6군락 4하위 단위로 구분되었다: A. 질경이 군락, A-a. 개망초 하위군락. A-b. 길뚝사초 하위군락. B. 큰개별꽃 군락, B-a. 대사초 군락. B-b. 가는네잎갈퀴 군락, C. 칡 군락, D. 조록싸리 군락, E. 산딸기 군락, F. 주름조개풀 군락. 이상의 군락을 구성하는 총 식물의 종류는 28과 83속 17변종 120종으로 조사되었다. 주요 출현 식물은 질경이, 개망초, 주걱망초, 칡. 조록싸리, 산딸기, 쑥, 제비쑥. 큰까치수염 등 주로 호광성이며 답압에 강한 식물들로 나타났다. 모든 조사구를 Bray-Curtis 서열법에 의해 서열화한 결과는 대체로 식물사회학적 표 조작에서 얻어진 결과와 유사하게 나타났다.

• 한국환경생태학회지
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• 제17권2호
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• pp.112-122
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• 2003

본 연구는 미동산의 관속식물상을 체계적으로 파악함으로써 충북지역 식물생태계 보전의 기초자료 제공과 아울러 희귀 및 멸종위기종에 대한 정확한 보전대책 수립 및 자생지복원을 위해 수행되었다. 충북 미동산(558m)의 관속식물상을 조사한 결과, 81과 215속 262종 38변종 3품종 등 총 303종류(Taxa)가 확인되었다. 희귀 및 멸종위기식물은 매미꽃, 층층둥글레 등 총 2 종류로 조사되었고 한국 특산식물은 가는장구채, 매미꽃, 조팝나무, 터리풀, 자란초, 병꽃나무, 숫명다래나무, 고려엉겅퀴, 분취 등 9종류로 나타났다. 또한 본 조사지역 내 출현한 귀화식물은 소리쟁이, 다닥냉이, 아까시나무, 붉은토끼풀, 토끼풀, 수박풀, 달맞이꽃. 돼지풀, 개망초, 망초, 서양민들레 방가지똥 등 총 12종류이다.

• The Korean Journal of Ecology
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• 제19권4호
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• pp.341-351
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• 1996

In order to elucidate the differences in early successional development among similary aged old-fields having different soil nitrogen (N), caused by the land use history before at abandonment, the response of plant community along an experimental nitrogen gradient (control plot (No), plot NI with 5.8g $N/m^2$, plot N2 with 11.7g $N/m^2$ and plot N3 with 23.3g $N/m^2$) was investigated in a five-year-old abandoned field. Although the N content in soil among treatments was similar at the end of the growing season, N concentrations in plant tissue increased with the amount of N supplied. These results suggest that almost all the N contained in N-enriched soil might be absorbed by plants during the growing season after N supply. Vegetation tended to grow vigorously by nitrogen supply, and the standing biomass increased significantly in plots NI and N2 . Species richness of plants, especially of annuals and perennials, was more reduced than the control plot, and the species diversity was also reduced by N supply. The importance value (IV) of species by N supply differed in each species along the position on the successional sere: Artemisia princeps var. orientalis as the dominant species in this old-field decreased slightly; annuals as the earlier successional species decreased clearly along nitrogen gardients; Erigeron annuals as the earlier successional species and as a strong competitor with Artemisia princeps var. orientalis had the highest IV by small N supply; Miscanthus sinensis and Rubus crataegifolius as the later successional species increased by large N supply. These results suggest that old-fields with high soil N might show the structural and functional characteristics of the earlier successional stages, but community composition in those old-fields might be changed more quickly from the sarlier successional species than the later successional species.

• 한국자원식물학회지
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• 제16권1호
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• pp.15-24
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• 2003

본 연구는 제주도 돼지 풀 군락군(Ambrosia artemisiifolia val. elatior community group)의 현존 식생을 파악하기 위해 식물사회학적 방법을 적용하여 실시되었다. 조사된 식물상의 총 출현종수는 48과 156속, 200종 28변종 2품종(귀화식물 20과 54속 69종 3변종 포함)이 생육하고 있다. 제주도 돼지풀 (Ambrosia artemisitfolia var. elatior)군락군은 개망초 - 큰망초군락(Erigeron annuus - Conyza sumatrensis community Miyawaki, 1982)과 환삼덩굴- 왕고들빼기 군집(Lactuco indicae - Humuletum japonicae Okuda, 1978), 개보리 - 울산도깨비 바늘 군락(Bromus tectorum - Bidens pilose community Miyawaki, 1982), 강아지 풀- 왕바랭이 군락(Setaria viridis - Eleusine indica community Miyawaki, 1982 )으로 대별되었다. 돼지풀은 해안에서 해발 1,500미터 한라산 영실까지 분포하고 있었다. 돼지풀의 우점도와 군도가 가장 높은 곳은 해발 345미터, 조천읍 선흘리 근처이며 ,가장 낮은 곳은 해발 1,020미터인 국립공원 서귀포시 영실, 근처이다.

• The Korean Journal of Ecology
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• 제14권2호
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• pp.211-230
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• 1991

The germinatin of e. annuus continued from the middle ofmay to mid-october. The maximum germination occurred on the mid-july. The period bloom of was distingushed amongs the different growth forms ; a orm pr of biennial and a form of pr perennial flowering from the mid-may to mid-september, and a form ps biennial blossom from the beginning of October to earlynovember. the dispersal of seed for(a form pr)occurred from early June to the mid-september. A rotte, germinating from summer to autumn, could classified into several growth forms; individuals without a critical leaf area for bolting until september and October, become a form ps of biennial, whicth did not proceed toreproductive growth unitl the next year, even thought wintering. individuals flowered on 3 years after germination become a form pr of perennial. The growth formular of aform pr of bennial, grown in a pot was w=20.2[1+$3.36{\times}10^3$(-0.062t)]$^{-1}$. The maximum relative growth rate(rgr) was 0.062g/g/day and the maximum net assimlation rate(nar) 0.089g/g/day. Therelative growth among each organ was shown as R=0.12 $T^{1.15}$between the avove-ground part(t) and the below- ground part(r). the relation between the avove-ground part(t) and the ratio of stem weight(wi) was ws/wi=2.56 $T^{0.35}$. n.p.k. was largely distributed on a leaf throughoutthe total growth period. while growing, it tended to decrease on the vegetative organ gut vice versa on the reproductive organ. however, nitrogen was more widely distributed on a leaf then in the reproductive organ.

• 한국환경복원기술학회지
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• 제4권1호
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• pp.1-15
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• 2001

The purpose of this study is to evaluate the creation techniques of eco-pond, one of biotopes to promote biodiversity in urban residence area. Investigation were classified out plant, mammals, amphibia, reptiles, birds, fishes and insects. The results were summarized as follows: Around the eco-pond shows simple vegetation structurs, consisted of Pinus densoflora S et Z. and Robinia pseudoacacia under competition. In case of shrub, consisted of 4 species but plant growing appearence diversely by seasons. The evaluation of vegetation of eco-pond, there are found 4 species of aquatic plants. Inside the revetment of pond, Echinochloa crus-galli, Persicaria hydropiper, Digiaria sanguinalis, Cyperus microiria and Bidens frondosa L. are mainly distributed. Near the revetment, Trifolium repens L. and Digiaria sanguinalis are prevailed. And in its background, Erigeron canadensis, Erigeron annuus and vines are begins to make their appearances. When evaluation animals in eco-pond and contrast plot, it show simple species and numbers of mammals. It seemed to be resulted from its isolation and outside intervention by users In eco-pond, Pica pica and Streptopelia orientalis are mainly found and in contrast plot of Columba livia, which are so strong adaptation to city life environment. In case of amphibia and reptiles, none is observed in contrast plot, but in ecological pond, Rana nigromaculata and Hyla japonica are constantly observed. In case of insects, more species are found in eco-pond than contrast plot. And in eco-pond, more dragonflies are visibly increased one year after its construction. In floral zone inside of pond revetment, grasshopper and Locusta migratoria are frequently observed. In case of butterflies, they are mainly found in log fence and willow(salix) around eco-pond. In case of fishes inside of eco-pond, the species and its density are remarkable increased one year after the construction. With above evaluation results, we have identify the increase effect of biodiversity after construction of the eco-pond.