• Journal of Forest and Environmental Science
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• 제26권3호
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• pp.181-192
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• 2010

Water erosion is progressing in the Loess Plateau, especially in gullies, and the sediment runoff to the Yellow River amounts to 975 million tons every year. Natural factors for water erosion include climate, soil, geological feature, terrain and vegetation. Many development projects due to the increasing population reduced the forest coverage ratio to 10%, and 200 million people in the downstream area are suffering from the damage during intense rainfall. Accordingly, the Chinese government is continuously trying to efficiently prevent the erosion by establishing measures for water erosion, including fish-scale pits, terrace technique, and check dams.

• 한국수자원학회:학술대회논문집
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• 한국수자원학회 2021년도 학술발표회
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• pp.316-316
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• 2021

Erosion in a watershed is one of the main sources of sediment inflow in dams. While sediment management practices can be performed to reduce and manage sedimentation in reservoirs, managing the sediment inflow before it reaches the reservoir should also be consider. The accurate location of areas with high erosion and deposition rates should be determined in order to propose an appropriate sediment management procedure such as the construction of check dams. In this study, the projected rainfall from HadGEMRA-3 for RCP 8.5, was used in C-SEM, a distributed rainfall-erosion model, to determine the projected spatial erosion patterns in Cheoncheon catchment, which is located in the upstream part of Yongdam Dam.

• Journal of Advanced Marine Engineering and Technology
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• 제23권5호
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• pp.695-701
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• 1999

Thermal sprayed Ni-Cr alloy coating on the carbon steel was carried out erosion-corrosion test and electrochemical corrosion test in the marine environment. THe erosion-corrosion behavior and electrochemical corrosion characteristics of substrate(SS400) and thermal sprayed Ni-Cr coating was investigated, The erosion-corrosion control efficiency of Ni-Cr coating to substrate was also estimated quantitatively.

• 대한전기학회:학술대회논문집
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• 대한전기학회 2002년도 학술대회 논문집 전문대학교육위원
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• pp.72-74
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• 2002

In this paper, we showed the erosion characteristics of MgO protector layer releated to lifetime of plasma display panel(PDP). We observed MgO erosion characteristic as a functions of deposition conditions. In RIE condition of Xe gas, the lowest erosion rate appears in the conditions of no heating, bias voltage -30V and pressure 5mtorr. In general. as deposition rate increases, erosion rate decreases.

• 한국산림과학회지
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• 제95권6호
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• pp.649-656
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• 2006

인공강우발생장치를 이용하여 4년간 대구 동구지역에 발생한 산불발생지를 대상으로 산불발생지사면의 토양침식량을 계량화하기 위하여 산불발생 후 경과년수에 띠라 각 지역에 대한 강우강도 및 경사별로 토양침식량을 관측하여 산불발생지의 토양침식 특성을 구명하고, 또한 토양침식량과 강우강도, 경사, 경과년수와의 관계를 분석한 결과는 다음과 같다. 1. 산불발생연도별 토양침식량은 강우강도가 30 mm/hr씩 증가함에 따라서 1.9~5.7배 증가하였고, 경사가 $10^{\circ}$씩 증가함에 따라서는 1.4~14.2배 증가하였다. 2. 산불발생당년에는 강우강도 80 mm/hr, 경사 $30^{\circ}$에 대해 초기 강우 10분 동안 토양침식이 많이 발생하였으며, 시간이 경과할수록 점차 그 양이 감소하는 경향을 보였고, 산불발생 후 2년 뒤부터는 강우강도 및 경사별로 경과시간에 따른 토양침식량은 거의 일정하였다. 3. 산불발생 후 경과년수에 따라 강우강도 및 경사별 토양침식량은 산불발생 3년 후의 경우 발생당년에 비해 28.9%~94.1%로 감소하였고, 산불발생당년에는 강우강도 및 경사별로 토양침식량이 많았으며, 산불발생 후 2년 뒤부터 점차 토양침식량의 감소추세가 둔화되었다. 4. 산불발생지사면에서의 토양침식량에 대해 각 인자간의 영향성을 분석한 결과, 강우강도, 경사, 경과년수의 각각의 주효과와 강우강도${\times}$경사, 강우강도${\times}$경과년수의 상호작용 효과에 대해서는 차이를 보였고, 경사${\times}$경과년수, 강우강도${\times}$경사${\times}$경과년수의 상호작용 효과에 대해서는 차이가 없었다. 토양침식량에 영향을 미치는 인자의 영향도는 강우강도가 가장 큰 영향을 미치고 다음이 경사, 경과년수의 순이었다. 5. 토양침식량과 이에 영향을 미치는 인자들과의 상관관계에 있어서, 강우강도, 경사간에는 1%수준에서 유의적인 정(+)의 상관관계가 있었고, 경과년수는 1%수준에서 유의적인 부(-)의 상관관계가 나타났다. 6. 토양침식량과 이에 영향을 미치는 인자들과의 회귀분석 결과, 산불발생지사면에서 토양침식량을 설명하는데 유의한 인자는 강우강도, 경사, 경과년수이었다. 7. 강우강도, 경사, 경과년수를 이용하여 다음과 같은 토양침식량 추정식을 산출하였다. S.E = 0.092R.I + 0.211D.S - 0.942E.Y(S.E : 토양침식량, R.I: 강우강도, D.S: 경사, E.Y: 경과년수)

• 한국산림과학회지
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• 제76권2호
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• pp.145-160
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• 1987

1966년(年)부터 1986년(年)까지 시행(施行)한 산지사방시행지(山地砂防施行地)의 사방공작물(砂防工作物)에 대한 파양상태(破揚狀態) 및 복구(復舊)의 필요성(必要性)등을 조사평가하기 위하여 사방설계기준단비(砂防設計基準單費)의 발전과정(發展過程) 및 현장시공지(現場施工地)를 조사(調査)하고 또 현행 재해대책사방제도(災害對策砂防制度)등을 검토(檢討)하였다. 당초 시공(施工)한 사방공작물(砂防工作物)의 약 10~15%가 보수(補修)가 필요하였다. 현재(現在)의 치산정책제도(治山政策制度)에서는 산지사방공작물(山地砂防工作物)이 풍수해(風水害) 등으로 파손(破損)당해도 예산미확보관계(豫算未確保關係) 등으로 인하여 "실제로" 복구불능(復舊不能)하므로 정규적(正規的)인 보수사방제도(補修砂防制度)(국비해대책예산사전확보(國費害對策豫算事前確保))를 신설(新設)해야 될 것이며, 특(特)히 "재해대책사방(災害對策砂防)"인 경우에는 피해규모(被害規模)에 불구하고 국비보수사방(國費補修砂防)이 가능(可能)하도록 제도화(制度化)되어야 할 것이다. 이 연구결과(硏究結果)는 앞으로 우리나라에서의 치산정책방향설정(治山政策方向設定)에 귀중한 정책자료(政策資料)가 될 것이다.

• 한국농공학회논문집
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• 제59권1호
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• pp.21-30
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• 2017

Soil erosion has been issued in many countries since it causes negative impacts on ecosystem at the receiving water bodies. Therefore best management practices to resolve the problem in a watershed have been developed and implemented. As a prior process, there is a need to define soil erosion level and to identify the area of concern regarding soil erosion so that the practices are effective as they are designed. Universal Soil Loss Equation (USLE) were developed to estimate potential soil erosion and many Geographic Information System (GIS) models employ USLE to estimate soil erosion. Sediment Assessment Tool for Effective Erosion Control (SATEEC) is one of the models, the model provided several opportunities to consider various watershed peculiarities such as breaking of slope length, monthly variation of rainfall, crop growth at agricultural fields, etc. SATEEC is useful to estimate soil erosion, however the model can be implemented with ArcView software that is no longer used or hard to use currently. Therefore SATEEC based on ArcView was rebuild for the ArcGIS software with all modules provided at the previous version. The rebuilt SATEEC, ArcSATEEC, was programmed in ArcPy and works as ArcGIS Toolset and allows considering monthly variations of rainfall and crop growth at any watershed in South-Korea. ArcSATEEC was applied in Daecheong-dam watershed in this study, monthly soil erosion was estimated with monthly rainfall and crop growth variation. Annual soil erosion was computed by summing monthly soil erosion and was compared to the conventional approach to estimate annual soil erosion. The annual soil erosion estimated by the conventional approach and by summing monthly approach did not display much differences, however, ArcSATEEC was capable to provide monthly variation of soil erosion.

• 한국환경복원기술학회지
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• 제1권1호
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• pp.133-140
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• 1998

The following conclusions are based upon data collected and visual observations made during the performance of the tests : 1. The performance of the erosion control products tested was for a particular set of conditions, and may be expected to differ if any or all of the test parameters were to be changed. If even just one parameter is changed from one test to the next, the results can be expected to be different. 2. Due to the fact that only two replications of each product were tested, we believe that the results presented herein are indicative only and not conclusive. 3. The ECB SC produced the least amount of soil erosion followed by ECB S, ECB C, and Coir No. 2, in that order. 4. All of the erosion control blankets tested significantly reduced soil erosion rates with respect to the bare soil controls. 5. The ECB S produced the smallest water runoff rate, followed closely by ECB SC. Next in order were ECB C and Coir No. 2. 6. All of the erosion control blankets reduced the water runoff rate with respect to the bare soil control. 7. Mesh 2cm There was not much difference in plant height for the four erosion control blankets and the bare soil control plots. the ECB S produced slightly taller plants than the rest of the materials tested. 8. The four erosion control blankets(ECB C, ECB SC, ECB S, and Coir No. 2) produced a larger plant mass than the bare soil plots. The difference between the plant mass for the four erosion control blankets, however, is minimal. 9. The ECB C produced the least percentage of lost seed and the largest percentage of germinating seed. 10. The ECB SC had the second smaller percentage of seed lost, followed closely by ECB S, and then by Coir No. 2. 11. All erosion control blankets had a smaller percentage of seed lost than the bare soil control plots. 12. The ECB C had the second largest percentage of germinating seed, followed closely by ECB SC and Coir No. 2. 13. All erosion control blankets had a larger percentage of germinating seed than the bare soil control plots. 14. The ECB C had the smallest percentage of non-germinating seed, followed by ECB S, Coir No. 2, and ECB SC, in that order. 15. All erosion control blankets had smaller percentages of non-germinating seed than the bare soil control plots.

• 한국해안·해양공학회논문집
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• 제33권6호
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• pp.246-256
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• 2021

연안을 중심으로 시행되는 각종 개발사업은 표사수지 불균형, 연안표사 이동상 및 횡단표사 이동상 변화를 야기하며, 이로 인한 해빈의 완충구간 축소로 연안재해 위험성을 크게 증대시킬 뿐 아니라 회복 불가능한 장기적 해안침식 문제를 초래하게 된다. 연안개발을 위해 건설된 각종 구조물의 영향으로 발생되는 장기적·지속적인 해안침식 현상은 표사수지 및 연안표사와 횡단표사 변화량 평가를 통해 직접적인 원인 규명이 가능하다. 즉, 표사수지 변화, 연안표사 이동, 횡단표사 이동 구분되는 이들 개별적인 원인에 기인한 침식지역과 복합적인 작용에 의한 침식지역의 분류를 통해 연안개발과 해안침식 현상의 인과성 평가가 가능할 것이다. 본 연구에서는 연안개발에 따른 침식 문제가 지속적으로 제기되고 있는 동해안(강원도, 경상북도) 일대 해안을 대상으로 연안 구조물 건설 및 육역 개발 등 주요 개발현황과 연안침식 실태조사 결과를 기반으로 장기적·지속적 침식원인을 분석하였다. 아울러 인공구조물 건설에 따른 침식의 정도를 평가하고자 침식 영향도 개념을 정립하고, 침식 영향도 평가를 위한 세 가지 방법론을 제안하였다. 연안침식 실태조사에서 검토된 해빈 영상분석 자료를 활용하여 하저항을 대상으로 침식 영향도를 평가하였으며, 평가결과 하저항 개발은 93.4%, 호안도로 건설은 6.6%로 침식에 영향을 미친것으로 평가되었다.

• 한국전산유체공학회지
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• 제16권2호
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• pp.66-74
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• 2011

The SCR catalyst in coal-fired power plant is eroded by the collision of fly ash on the catalyst surface. However the erosion of SCR catalyst by the collision of fly ash has not been fully studied, especially in terms of fluid dynamics. Hence, in the present study, we focus on the gas and solid flows inside the SCR catalyst duct and their consequent effect on the erosion characteristics. For this purpose, computational fluid dynamics is applied to investigate the two-phase flows and to evaluate the erosion rate for different flow and particle injection conditions. Also, the erosion rate and pressure drop of commonly used square shape are compared with equilateral triangle and hexagon shapes. The pressure drop of SCR catalyst is increased when SCR catalyst surface area per unit volume increases. The erosion rate of SCR catalyst is enhanced when the particle velocity, mass flow rate of particle, particle diameter and cell density of SCR catalyst are increased. From the results, the pressure drop and erosion rate at the catalyst surface can be minimized by reducing cell density of SCR catalyst to decrease particle velocity and number of particle impacts.