• Proceedings of the Plant Resources Society of Korea Conference
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• 2022.09a
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• pp.65-65
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• 2022

지속가능한 DMZ 일원의 생태복원 추진을 위해 DMZ 생태교란지에서 복원공법 모니터링을 실시하였다. 본 실험은 강원도 인제군, 철원군 및 경기도 연천군의 DMZ 내(450m²)에서 진행되었으며, 흰민들레, 구절초, 매발톱, 질경이, 꿀풀이 공시식물로 사용되었다. 각 대상지의 식생유형별 시공방법에 따른 침입종 억제효과를 알아보기 위해 2022년 4월부터 9월까지 일반식생기반재와 특수식생기반재로 처리된 실험구의 전체 피도, 도입종 피도, 침입종 피도, 초장, 출현종 등을 측정하였다. 전체 피도는 세 곳 모두 일반 기반재보다 특수기반재에서 더 높게 나타났으나 대상지에 따라 침입종 피도가 미치는 영향은 달랐다. 도입종의 피도는 인제, 철원, 연천에서 동일하게 흰민들레가 가장 높은 수치를 보였고, 특수기반재에서 보다 높은 피도를 보였다. 폭염 및 폭우로 6월 이후 흰민들레가 감소하면서 구절초, 매발톱의 피도가 점차 증가하였으며 기반재 간의 큰 차이는 없었으나 일부 지역에서는 구절초 피도가 특수기반재보다 일반기반재에서 더 높게 나타났다. 또한, 모든 지역에서 질경이와 꿀풀의 생장은 미미하였다. 같은 처리를 했음에도 대상지별로 소재식물의 출현 여부, 생장률, 침입종의 피도 등이 다른 것으로 보아 복원지의 환경 여건에 따라 적용해야 하는 종, 시공방법, 주변 완충지역의 범위 등에 차이를 두어야 할 것으로 보인다.

• Journal of Korean Society of Forest Science
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• v.109 no.3
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• pp.249-258
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• 2020

The purpose of this study examined the succession by vegetation type after forest ecosystem restoration in the Baramjae area. Vegetation of the Baramjae area was classified using a survey of 81 sites from May to October 2019. The vegetation type was classified as Pinus densiflora community group with both Quercus mongolica community and P. densiflora typical community. The group unit was further classified as the Quercus dentata typical subgroup, Salix koreensis subgroup, and Q. mongolica typical subgroup. Such as Q. mongolica, Quercus variavilis in vegetation unit 1, Q. mongolica, Q. dentata in vegetation unit 2, P. densiflora in vegetation unit 3 and S. koreensis in vegetation unit 4 were shown a high importance value. The difference in species by vertical layer is explained by sere. Based on the vegetation type classification system, Detrended Correspondence Analysis was conducted to observe the trend of succession. Since restoration, vegetation unit 1 and vegetation unit 2 were considered to have developed the most extensive vegetation. In vegetation unit 2 and vegetation unit 4, many of the species found were in the early vegetation development in S. koreensis subgroup. Accordingly, vegetation in the Baramjae area can be categorized as a stepwise succession.

• KSCE Journal of Civil and Environmental Engineering Research
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• v.29 no.3B
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• pp.247-257
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• 2009

In the present paper, turbulent open-channel flows with alternate vegetated zones are numerically simulated using threedimensional model. The Reynolds-averaged Navier-Stokes Equations are solved with the ${\kappa}-{\varepsilon}$ model. The CFD code developed by Olsen(2004) is used for the present study. For model validation, the partly vegetated channel flows are simulated, and the computed depth-averaged mean velocity and Reynolds stress are compared with measured data in the literature. Comparisons reveal that the present model successfully predicts the mean flow and turbulent structures in vegetated open-channel. However, it is found that the ${\kappa}-{\varepsilon}$ model cannot accurately predict the momentum transfer at the interface between the vegetated zone and the non-vegetated zone. It is because the ${\kappa}-{\varepsilon}$ model is the isotropic turbulence model. Next, the open channel flows with alternate vegetated zones are simulated. The computed mean velocities are compared well with the previously reported measured data. Good agreement between the simulated results and the experimental data was found. Also, the turbulent flows are computed for different densities of vegetation. It is found that the vegetation curves the flow and the meandering flow pattern becomes more obvious with increasing vegetation density. When the vegetation density is 9.97%, the recirculation flows occur at the locations opposite to the vegetation zones. The impacts of vegetation on the flow velocity and the water surface elevation are also investigated.

• Proceedings of the Korean Geotechical Society Conference
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• 2010.03a
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• pp.1334-1341
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• 2010

유망식생공을 실시한 사면에 집중강우가 유입되면 단위중량이 증가하여 중력방향으로 이동을 하게 되며, 그에 따라 망이 유실되는 경우가 많아, 이를 고려한 점착력 확보가 요구되고 있는 실정이다. 강우와 사고사례에 따른 분석을 통하여 적절한 점착력을 확보하기 위한 기준마련 및 제시를 통해 국도이용의 안정성을 확보하고자 한다.

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2016.10a
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• pp.235-235
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• 2016

• Proceedings of the Korean Society of Environment and Ecology Conference
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• 2000.04a
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• pp.70-74
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• 2000

• Proceedings of the Korean Society of Environment and Ecology Conference
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• 2000.04a
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• pp.79-83
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• 2000

• Proceedings of the Korean Society of Environment and Ecology Conference
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• 2000.04a
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• pp.165-167
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• 2000

• Proceedings of the Korean Society of Environment and Ecology Conference
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• 2004.04a
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• pp.101-105
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• 2004

• Proceedings of the Korean Society of Environment and Ecology Conference
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• 2004.04a
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• pp.179-183
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• 2004