• 한국수자원학회논문집
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• 제40권2호
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• pp.183-190
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• 2007

본 연구에서는 식생여과대에 있어서 토양층의 역할에 주목하였으며, 토양 침투량이 증가될 수 있는 구조로 토양층을 변형하여 일반적인 식생여과대에서의 오염저감효과와 비교 분석하였다. 따라서 연구의 최종 목적은 토양층 변화를 통한 식생여과대의 수질개선효과를 일반적인 토양층으로 구성된 식생여과대와 비교, 검토함으로써 보다 효과적인 식생여과대를 조성하고자 하는 것이다. 실험분석 결과, 토양층 변화를 접목시킨 식생여과대는 일반 식생여과대에 비해 표면유출에서 높은 오염물질 저감효과가 있는 것으로 나타났다. 이는 표면유출수 일부가 정류벽을 통과한 후 재상승하여 표면으로 유출되었기 때문으로 판단된다. 그러나 계단형에서의 하부유출수의 경우, 입경이 큰 모래와 자갈을 통과하여 유출이 일어나기 때문에 직선형 식생여과대보다 오염저감효율은 다소 낮게 나타났다. 이를 오염물질 유출부하량의 개념으로 파악해 보면, 하부유출량이 전체 유출유량에 대한 기여도가 계단형(4%)에서 직선형(2%)보다 높기 때문에 계단형에서의 오염물질 저감부하량이 직선형에 비하여 매우 높게 나타났다. 따라서 정류벽과 표면층 변화를 통해 침투량을 증가시킨 식생여과대는 일반적인 식생여과대보다 저감효과가 크고 식생여과대 적용에 필요한 여러 조건(토양의 침투성, 여과대의 넓이 및 길이, 유속 등)을 만족하지 않더라도 충분한 저감효과를 발휘할 수 있을 것으로 기대된다.

• 한국환경과학회지
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• 제12권6호
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• pp.605-613
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• 2003

In order to make use of the protection effect against wind by the vegetation, it examined whether it should make what vegetation form and arrangement using the 2-dimensional non-hydrostatic model. When the foliage shielding factor increases, it becomes hard to take in protection effect against wind in a residential section. When it makes height of vegetation high, it becomes hard to take in protection effect against wind with height. In the comparison in the case where vegetation high is gradually made low toward wind-stream from a vegetation, and the case of making it low gradually, although former tends to receive the protection effect against wind by the vegetation, attenuation of wind velicity becomes large. In the comparison in the case where foliage shielding factor and distribution of density of leaf are gathered gradually toward wind-stream from a vegetation. It has been understood to evaluate to height the influence that the vegetation multi-layer model by which the heat revenue and expenditure in the direction of the vegetation height is considered is used, and to characterize the vegetation group by the parameter setting.

• 한국환경복원기술학회지
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• 제22권1호
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• pp.47-59
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• 2019

This study was composed of four treatments [no treatment, phosphate + limestone layer treatment, phosphate + sodium bicarbonate + cement layer treatment, and phosphate + sodium bicarbonate + limestone layer treatment] for figuring out vegetation effects on the acid drainage slope. Treated acid neutralizing techniques were effective for neutralizing acidity and vegetative growth in order of [first: phosphate + sodium bicarbonate + limestone layer treatment, second: phosphate + sodium bicarbonate+cement layer treatment, third: phosphate + limestone layer treatment and fourth: no treatment] on the acid drainage slope. We found out that sodium bicarbonate treatment was additory effect on neutralizing acidity and increasing vegetaive growth besides phosphate and neutralizing layer treatments. In neutralizing layer treatments, Limestone layer was more effective for vegetation and acidity compared to cement layer treatment. Cement layer showed negative initial vegetative growth probably due to high soil hardness and toxicity in spite of acid neutralizing effect. Concerning plants growth characteristics, The surface coverage rates of herbaceous plants, namely as Lotus corniculatus var. japonicus and Coreopsis drummondii L were high in the phosphate + sodium bicarbonate + limestone layer treatment while Festuca arundinacea was high in the phosphate + sodium bicarbonate + cement layer treatment. We also figured out that soil acidity affected more on root than top vegetative growth.

• 한국자원식물학회:학술대회논문집
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• 한국자원식물학회 2019년도 춘계학술대회
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• pp.90-90
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• 2019

This study was carried out to investigate the vegetation and vegetation structure of Mt. Man in Hwacheon Gun from April to October 2018. The survey site is located in the northern part of South Korea where the climate is similar to that of North Korea. The purpose of this study is to provide basic information for efficient ecological forest management after unification. A total of 341 vascular plant taxa are recorded, representing 221 genera, 4 subspecies, 42 varieties and 6 forms in 84 families. Rare species, including Crataegus komarovii and Amitostigma gracile are found across 10 taxa; 8 families, 10 genera, 9 species, 1 variety. Naturalized Plants, including Ambrosia artemisiifolia and Erigeron annuus found across 11 taxa; 6 families, 10 genera, 11 species. Dominant tree species of the tree layer based on the highest importance values were: Quercus mongolica (23.47%), Larix kaempferi (11.43%), Fraxinus rhynchophylla (8.30%), in the subtree layer were: Lindera obtusiloba (11.38%), Acer pictum subsp. mono (11.33%), Fraxinus rhynchophylla (9.80%) and in the shrub layer were: Lindera obtusiloba (10.22%), Fraxinus rhynchophylla (8.43%), Rubus crataegifolius (8.00%), in the herb layer Pteridium aquilinum var. latiusculum (5.67%), Oplismenus undulatifolius (5.00%), Lysimachia clethroides (3.49%) respectively. The species diversity of Mt. Man was 1.1764 in the tree layer, 1.2403 in the subtree layer, 1.4135 in the shrub layer, and 1.7416 in the herb layer. In conclusion, if we utilize the flora and vegetation structure surveyed in Mt. Man, we can effectively manage the degraded forests with similar altitudes and climate zones in North Korea.

• 대한토목학회논문집
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• 제39권2호
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• pp.307-316
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• 2019

하도 내 식생발달은 흐름저항을 크게하여 홍수 시 하천 수위를 상승시키고 수위-유량관계의 변화에도 영향을 미치고 있다. 홍수 시 수위가 첨두에 도달하고 하강하여 하도 내 드러난 식생은 대부분 도복(倒伏, prone) 상태에 있다. 이렇게 식생이 도복상태로 되어있는 식생층 구간은 식생된 개수로 흐름의 유속분포를 고려하였을 때 유속이 0인 지점의 높이로 고려된다(Stephan and Guthnecht, 2002). 그러나 부자 측정에 의한 유량산정에 있어서 식생층 구간의 높이를 고려하지 않고 하상높이를 유하면적으로 적용하면 유량이 과대 산정되는 경향이 발생한다. 본 연구에서는 식생된 하천에서 정도 높은 유량을 산정하기 위해 영강의 점촌, 내성천의 향석 지점에서 홍수 후 식생층 높이를 측량하고 통수단면적에서 식생층 투영면적을 제외하여 유량을 산정하였다. 그 결과, 유량의 규모에 따라 차이는 있지만 최소 4.34 %에서 최대 10.82 %의 유량편차를 보였다. 따라서 홍수 시 통수단면적을 적용하여 유량을 산정하는 유속-단면적 방법에 있어서 식생하천에서 식생층 높이의 투영면적을 고려하여 유량을 산정한다면 좀더 적합한 유량산정이 이루어질 것으로 판단된다.

• 한국농공학회:학술대회논문집
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• 한국농공학회 2003년도 학술발표논문집
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• pp.219-222
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• 2003

Bech scale tests were performed to evaluate the adaptability of industrial wastes, especially bottom ash, salg and phosphogypsum among others, for constructing the surface layer of a landfill or reclamation, which function is a vegetation base layer. In the test, columes test were used to check the extraction characteristics of wastes and small PVC soil-box that equipped the drainage device was used to model a performance of layers and to monitor the growth of plants at the composite layer of those. Tests have been continued during one and half year and It has been verified that bottom ash and phosphogypsum look like as a valuable material to safely reuse as the vegetation base layer even though some unconfined factors are remain.

• 한국조경학회지
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• 제14권3호
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• pp.21-31
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• 1987

The overuse in the outdoor recreation lands has been deteriorating the natural resources and landscapes. So this study was executed to measure the users'impacts on vegetation and soil at Hwaum Temple District Campsite in the Mt. Jiri National Park, the southern part of Korea. Five sites were sampled in the study area according to the extent of impact observed. Then the users'densities and impacts on vegetation and soil were measured at each site. According to the result of this study, the numbers of species and individuals and the coverage of lower-layer vegetation showed outstanding changes by only light use. The numbers of species and individuals of middle-layer vegetation, species diversity indices, change rate in species composition of lower and middle-layer vegetation, damage rate of forces, contents of clay, soil moisture and organic matters, exchangeable base ions, soil hardness, organic matter depth and bare area of the campsite showed conspicuous changes from the site 4(19.6men / 1,000㎡). Especially, the self-repair of vegetation was impossible as the result of analysis of soil hardness and the formation of natural vegetation was expected to be difficult as the result of vegetation sturcture analysis over the users'average density of 19.6men /1,000㎡. The campsite management of this area shall be proposed as follows to prevent serious deterioration of natrual environment. A limitation of the present use and a conservation on soil and vegetation should be required at the site 4 and 5. Specially, prevention of camping recreation and artificial rehabilitation are necessary at the site 5(24. 3 men/1000㎡)

• 한국전자파학회논문지
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• 제27권7호
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• pp.660-663
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• 2016

본 논문에서는 초목 층 산란모델과 지표면 산란 모델을 이용하여 초목 층에서 수분함유량 측정에 초목 층과 레이다 파라미터가 갖는 영향에 대하여 분석하였다. $1^{st}$-order RTM(Radiative Transfer Model)을 이용하여 여러 상태의 초목 층 밀도와 입사각, 주파수, 편파를 갖는 데이터베이스를 생성하고, WCM(Water Cloud Model)과 Oh 모델을 이용하여 후방산란계수로부터 지표면 수분함유량을 추출하였다. 수분함유량 추출 에러를 예측하기 위해 추출한 수분함유량과 RTM의 입력 변수인 수분함유량을 비교하였다. 수분함유량 추출 에러로부터 초목 층에서의 수분함유량 측정에서 초목 층 밀도와 입사각, 주파수, 편파에 따른 초목 층과 레이다 파라미터의 영향을 분석하였다.

• 환경영향평가
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• 제19권3호
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• pp.231-245
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• 2010

The the purpose of this study was to analyze of the vegetation structure and phytosociological changes in the area adjacent to GeumJeong Mountain Fortress for fifteen years. The result of this study was as follows; Of the 8 quadrates, site of the North Gate 2 was having a highest in the number of extinct trees, 15 kinds. This is probably due to trampling effect caused by climbers' steps. Site of the West Gate 1 and South gate 1 each had 8 kinds of extinct trees, respectively. The number of newly appeared trees was highest at site of the North Gate 1, (8 kinds) followed by the sites of South gate 1 and South gate 2, respectively (5 kinds). The highest decrease in number of tree species was observed in North Gate 1, therefore, there is a strong relationship between vegetation diversity and the number of users of the available spaces. In order to revitalize the unstable vegetation structure of the Area Adjacent to GeumJeong Mountain Fortress, Robinia pseudo-acacia has to be well maintained in the shrub tree layer, and vines, such as Smilax china, Humulus japonicus, and Pueraria thungergiana, should be removed. To recover natural vegetation, dead leaf layer should be protected, and more shrub trees need to be planted. In the understory and shrub tree layer, multi layer tree planting is highly recommended to recover natural vegetation and increase tree diversity. In order to improve bad soil condition caused by trampling effect of recreational users, special treatments to the soil structure are required, such as mulching and raking soil. Also, depending on its soil damage from users trampling, the areas in the park should be divided into usable areas and user limited areas by the sabbatical year system. To improve the soil acidity due to acidic rain, soil buffering ability should be improved by activating microorganisms in the soil by using lime and organic material.

• 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.