• 한국산림과학회지
• /
• 제101권2호
• /
• pp.251-258
• /
• 2012

2009년부터 2011년까지 3년간 국유림내 사방시설 점검대상지에 대하여 현장점검을 실시하고 그 결과를 분석하였다. 대상지는 총 1,628개소로 사방댐 308개소, 사방지 1,320개소(1,269.05 ha)였으며, 현장조사는 연도별로 3~6월 사이에 실시하였다. 점검대상 사방댐은 1991년~2005년에 시공되었으며 96.4%인 297개소가 2000년 이후에 시공된 것으로 나타났고, 사방지는 1986~2005년에 시공되었으며, 68.6%인 903개소가 2000년 이후에 시공된 것으로 나타났다. 사방댐은 콘크리트댐과 콘크리트전석댐이 각각 205개소와 68개소로 많았으며, 총 308개소의 사방댐 중 296개소가 양호한 것으로 나타났다. 사방지에는 돌쌓기와 돌망태를 이용한 사방구조물이 많이 시설되어 있었으며, 총 1,320개소 중 1,245개소(94.3%)가 양호하였다. 전체적으로 국유림내 사방시설은 양호한 상태를 나타내어 그 기능을 충분히 발휘하고 있는 것으로 나타났다. 사방시설 중 불량한 상태인 것으로 나타난 경우 반드시 보완 보수를 통해 사방사업의 목적이 달성될 수 있도록 해야 할 것이다. 또한 기존 사방시설과 향후 사방사업으로 시공되는 사방시설의 체계적인 유지 및 관리를 위해서는 사방시설 관리 시스템의 구축이 시급하다.

• Journal of Forest and Environmental Science
• /
• 제12권1호
• /
• pp.13-25
• /
• 1996

최근의 사방사업(砂防事業)은 방재공간(防災空間)의 확보뿐 만 아니라 주변환경(周邊環境)에 잘 조화되고 생물자원(生物資源)이 풍부한 환경공간(環境空間)의 확보가 강조되고 있다. 일본에서도 이와같은 노력이 1990년대에 들어 활발히 진행되고 있으므로 우리나라의 사방사업의 참고가 될 수 있도록 일본의 친환경적(親環境的) 사방사업(砂防事業)에 대한 자료를 수집, 분석하였다. 구체적인 내용은 합리적인 수변환경(水邊環境) 조성(造成)과 친환경형(親環境型) 사방사업(砂防事業)이며, 친환경적(親環境的)인 사방사업(砂防事業)은 사방(砂防)댐, 유로공(流路工)과 호안공(護岸工), 어도(魚道) 및 수질보전공(水質保全工) 등에 대하여 정리하였다.

• 한국산림과학회지
• /
• 제20권1호
• /
• pp.51-60
• /
• 1973

The trend and achievments of soil erosion control research in Japan were investigated through observation tours and reference work and following facts were found to be important aspects which should be considered in the soil erosion control research program in Korea. Experiments on forest and water relations, and ground water phenomena at the water source zone in Tokyo University. Studies on land-slides and erosion control dam in Kyoto University. Studies on mud-flow and snow avalanches in Hokkaido University. Studies on sanddune fixation and disaster damage prevention forests in Kyushu University. Studies on forest denudations in Nagoya University. Studies on Greening-works and soil erosion prevention chemicals in Tokyo Agriculture University. Training on planning of erosion control works and prevention of disaster damages in Forest Research Institute. Experiments on soil erosion phenomena and infiltration in Tohoku Branch, FRI. Experiments on erosion and surface stratum failure of steep slopes and their prevention methods in Railway Technical Research Institute.

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

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

• 농업과학연구
• /
• 제37권2호
• /
• pp.223-229
• /
• 2010

This study is to analyze location conditions for erosion control dams to be constructed in Chungcheongnam-do, Daejeon Metropolitan City, Chungcheongbuk-do and Gyeongsangbuk-do in order to establish proper conditions for erosion control dams in the future. 199 sites where erosion control dams are expected to be built in 2010 were chosen and investigated in terms of 12 factors including basin area, basin slope, and landslide risk. The results showed that erosion control dams for Chungcheongnam-do and Daejeon Metropolitan City are mostly impermeable gravity dams mainly composed of concrete. In contrast, Chungcheongbuk-do and Gyeongsangbuk-do are increasing the number of permeable or compound erosion control dams. Basin analysis at planned erosion control dam sites showed that at least 44.5% of the total area has high landslide risk. Gyeongsangbuk-do had the largest basin area for erosion control dam sites at 157.3ha, followed by Chungcheongbuk-do at 64.4ha and Chungcheongnam-do at 54.8ha. Analysis of sand deposits in the Chungcheongnam-do erosion control dam built in 2010 confirmed an average deposit of 971.8m3. The sand deposit capacity and amount of sediment control for erosion control dams have a very low correlation with basin area or flow path slope, and this needs to be addressed in future sand deposit capacity designs.

• 한국지반공학회:학술대회논문집
• /
• 한국지반공학회 2010년도 춘계 학술발표회
• /
• pp.911-920
• /
• 2010

A closed-type erosion control dam were suggested as an effective method to protect from debris flow damages caused by seasonal rainstorm, typhoon, and local heavy rain. However, design method on a closed-type erosion control dam currently practiced in the engineering is not well established with respect to type of the dam, design parameters, maintenance and so forth. In this study, design parameters for closed-type erosion control dam were evaluated and the comparison of design parameters used in Korea and Japan was performed. Based on the results of this study, modification of design method for closed-type erosion control dam are recommended.

• 농업생명과학연구
• /
• 제50권5호
• /
• pp.111-120
• /
• 2016

본 연구는 경남지역 야계사방사업지의 적지적소를 판정하기 위해 사방댐 총 526개소와 계류보전시설 총 230개소의 기시공지 및 시공예정지를 대상으로 입지 및 임상, 수문조건을 분석하였다. 사방댐 시공지과 계류보전시설은 입지환경인자 중 퇴적암, 표고 201~400m, 경사 21~30°, 산사태위험등급 2등급인 곳에 가장 많이 시공되었고, 임상환경인자인 임상, 경급, 영급, 밀도 중 소경급, III영급 임분에서만 시공빈도가 유사하였다. 또한 사방댐의 크기 및 개소수를 결정하는 수문환경인자 중 유역면적의 경우 50ha 이하, 수계밀도 2.1~4.0km/㎢, 종장형 수계, 1시간당 최대강수량 61~90mm, 1일 최대강수량 201~300mm인 곳에서 가장 많이 시공되었다. 따라서 사방댐 시공지와 계류보전시설지 간의 입지 및 수문조건이 다소 유사한 것으로 추후 야계사방사업을 실시할 경우 산각붕괴 및 침식 발생위험이 높은 지역에 한해서는 사방댐과 계류보전시설의 병행이 가능한 것으로 판단된다.

• 한국환경복원기술학회지
• /
• 제3권3호
• /
• pp.113-125
• /
• 2000

This study was carried out to introduce current status and development strategy for an environmental restoration of stream side in Japan, and to consider a methodology which could be effectively applied for the environmental restoration of stream side in Korea. The strategy prospects of environmental restoration in Japan were summarized as follows : 1. When we establish the long term erosion control planning, we should make detail planning after considering of a certain block of watershed units. Because most of the disaster is caused by soil movement which was occurred by water contents. 2. Nowadays, the general torrent erosion control planning system in Japan focused on reducing the sediment such as by placement of erosion control facility and by restoration of afforestation, after calculation of several factors including expected amount of sediment, and the different amount of planned sediment and allowable sediment. 3. In the past, the goal of forest conservation and erosion control planing was to fix the amount of soil movement by construction of permanent facilities. While, the goal of forest conservation and erosion control planning in the future needs to change the techniques to a small and middle scale's soil movement which could prevent soil movement from large scale of soil disasters, but allow soil movement effectively. Also, it is considered to change erosion control dams from non passing type to passing type. 4. Restoration of stream-side ecology, erosion control for the conservation of ecology should be planned and conducted cautiously based on concepts of ecology conservation and development of environmentally sound techniques.

• 농업과학연구
• /
• 제47권4호
• /
• pp.803-814
• /
• 2020

Managing erosion control dams requires the annual average sediment yield to determine their storage capacity and time to full sediment-fill and dredging. The GeoWEPP (Geo-spatial interface for Water Erosion Prediction Project) model can predict the annual average sediment yield from various land uses and vegetation covers at a watershed scale. This study assessed the GeoWEPP to determine the annual average sediment yield for managing erosion control dams by applying it to five erosion control dams and comparing the results with field observations using ground-based LiDAR (light detection and ranging). The modeling results showed some differences with the observed sediment yields. Therefore, GeoWEPP is not recommended to determine the annual average sediment yield for erosion control dams. Moreover, when using the GeoWEPP, the following is recommended :1) use the US WEPP climate files with similar latitude, elevation and precipitation modified with monthly average climate data in Korea and 2) use soil files based on forest soil maps in Korea. These methods resulted in GeoWEPP predictions and field observations of 0 and 63.3 Mg·yr-1 for the Gangneung, 142.3 and 331.2 Mg·yr-1 for the Bonghwa landslide, 102.0 and 107.8 Mg·yr-1 for the Bonghwa control, 294.7 and 115.0 Mg·yr-1 for the Chilgok forest fire, and 0 and 15.0 Mg·yr-1 for the Chilgok control watersheds. Application of the GeoWEPP in Korea requires 1) building a climate database fit for the WEPP using the meteorological data from Korea and 2) performing further studies on soil and streamside erosion to determine accurate parameter values for Korea.