• 한국환경복원기술학회지
• /
• 제3권1호
• /
• pp.1-9
• /
• 2000

The purpose of this study was to analyze the characteristics of soil erosion on the fill-slope of forest road by elapsed years after road construction. Thirteen plots were established on the fill-slope of the newly-constructed forest road, and surveyed for two years(1997~1998). In these plots, the data about soil erosion, surface runoff, vegetation coverage, slope structural characteristics and rainfall were collected. In 1997, the major causes for soil erosion were found by the correlation coefficients with the amount of surface runoff from the fill-slope, vegetation coverage, slope length, slope degree, total rainfall and max. 1 hour rainfall. But, in 1998, the major causes for soil erosion were vegetation coverage and slope degree. Using the stepwise multiple regression method, in 1997, the amount of soil erosion from the fill-slope was complexly expressed as a exponential function of statistically significant the amount of surface runoff from the fill-slope, total rainfall, slope degree of fill-slope and vegetation coverage, but, in 1998, simply expressed as a exponential function of vegetation coverage.

• 한국산림과학회지
• /
• 제84권3호
• /
• pp.319-332
• /
• 1995

이 연구는 임도구조(林道構造) 및 강우(降雨) 특성(特性)이 신설임도(新設林道)에서의 초기침식(初期浸蝕)에 미치는 영향(影響)을 구명(究明)하고, 임도신설구역(林道新設區域)에서의 침식량(浸蝕量)을 파악(把握)하기 위하여 서울대학교(大學校) 농생대(農生大) 부속(附屬) 남부연습림(南部演習林) 자운산(自雲山) 지구(地區)에 임도(林道)가 개설(開設)된 구역(區域)을 대상으로 임도신설(林道新設) 직후 2년동안 초(初) 성토사면(盛土斜面), 노면(路面), 측구(側溝) 등 임도(林道) 각(各) 구조부(構造部)에서 발생(發生)되는 침식량(浸蝕量)과 강우(降雨) 및 임도구조(林道構造) 인자(因子)와의 관계(關係)를 조사(調査) 분석(分析)하였다. 임도(林道) 각(各) 구조부(構造部)의 설계(設計) 인자(因子)의 조합(組合)으로 이루어진 다종회귀식(多種回歸式)들은 임도(林道) 각(各) 구조부별(構造部別) 침식량(浸蝕量) 변동(變動) 설명(說明)에 유의(有意)하였다. 이 임도개발구역(林道開發區域)에서 임도신설후(林道新設後) 2년간(年間)(1993~1994)의 임도(林道) 1km당(當) 총침식량(總浸蝕量)은 658.51m/km였으며, 임도(林道) 초기침식량(初期浸蝕量)의 약 21.9%(144.27m/km)는 초기사면(初期斜面)에서, 39.8%(261.89m/km)는 성토사면(盛土斜面)에서 8.1%(53.33m/km)는 노면(路面)에서, 30.2%(199.02m/km)는 측구(側溝)에서 발생되었다.

• 한국환경복원기술학회지
• /
• 제3권2호
• /
• pp.66-74
• /
• 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. We should establish a new paradigm of forest road, forest conservation and erosion control which can emphasize the restoration of the streamside ecosystem and reduce the effects of soil movement change in the areas. And we should maintain the biotic habitats to conserve native biotic community when we practice forest road, forest conservation and erosion control works. 2. In the point of view ecological conservation aspects, we should evaluate the effects of new forest conservation and erosion control methods which is emphasized on the restoration of the streamside ecosystem to apply desirable methodology to the environmental restoration of the streamside area. 3. In the past, the objective of forest conservation and erosion control was to fix a soil by construction of permanent structures. Whereas, the direction of future's forest conservation and erosion control needs to change new forest conservation and erosion control technology to prevent large scale soil movement but allow small scale soil movement to conserve sound ecosystem and biotic habitats. 4. The restoration of the streamside ecosystem should provide continuity of the streamside environment which allows desirable biological habitats, and environmentally sound facilities to harmonize the environment.

• 한국환경복원기술학회지
• /
• 제2권3호
• /
• pp.83-92
• /
• 1999

To investigate the influence of forest road characteristics and site conditions on the stability of forest-road in granite area, four forest roads had been selected in Kyongbuk regions. The total of 13 road characteristic variables were evaluated by the discriminant analysis. The factors influencing the stability of forest road were bed rock, slope length, coverage, hardness, side-ditch erosion and road width. But aspect and soil texture were not significant for the stability in this area. In the correlation between forest environment and road structure, hardness and bed rock was highly significant in stability group, and coverage and side-ditch erosion was highly significant in instability group. 75 of 175 segments were instable whereas the others were stable. The centroids value by discriminant function in the stability and instability were estimated to 3.0585 and -1.9116, respectively. The stability criterion of forest road was discriminated from the centroids value of the each group. The main factors contributing the stability of forest road were significant in order of side-ditch erosion, coverage, soil texture, elevation, gradient, slope length and construction year. The prediction rate of discriminant function for stability evaluation of forest road was as high as 97.44%. In conclusion, the forest road structure factors such as length, coverage and slope gradient were controlled by construction techniques. If the factors like those should be considered in design, construction and forest road management, the stability of forest road may increase more. And also, it is necessary to take slope protection measures like small terraces and retaining walls for stability of cut slope.

• 한국환경복원기술학회지
• /
• 제11권5호
• /
• pp.92-103
• /
• 2008

Development of new approaches to achieve naturally good ecological potential of forest road cut-slope by making the best use of advantages of gabion systems with vegetation base materials to prevent slope failure and erosion, in the area with highly erodible soil. As a result on the type analysis of gabion systems already installed in road cut-slopes, gabion systems were generally established to prevent slope failure. Existing gabion systems can be divided into monolithic and modular system and can be divided into ten subtypes according to the purpose of establishment and combination of other measures. As a result on the monitoring of erosion amount from forest road cut-slopes in the test applications, the order of erosion amount from largest to smallest is as follows : the curved road cut-slope site where normal gabion system was established ($7,911cm^3$); the control site ($7,632cm^3$); the straight road cut-slope site where normal gabion system was established ($7,301cm^3$); the curved road cut-slope site where the new gabion system was established ($5,684cm^3$); and the straight road cut-slope site where the new gabion system ($5,325cm^3$). Therefore, the result shows that the new gabion system is more effective than the normal gabion system to reduce erosion amount from forest ! road cut-slopes. During the study period, vegetation coverages of the straight and curved road cut-slope site where the new gabion system was established were about 45% and about 36%, so average vegetation coverage of the sites where the new gabion systems was established was higher than the sites where the normal gabion systems was established. Therefore, it was concluded that the new gabion system can be more effective for cut-slope revegetation.

• 한국산림과학회지
• /
• 제76권2호
• /
• pp.161-168
• /
• 1987

임업기계훈련원(林業機械訓練院)에서 1984년(年) 시범적(示範的)로 임도(林道)를 시설(施設)(10 km)할 목적(目的)으로 10 km를 시공(施工)했는데 1986년(年) 태풍(颱風) 내습시 부분적(部分的)으로 노견붕괴(路肩崩壞)와 측구침식(側溝浸蝕)이 발생(發生)하였다. 이에 대한 원인(原因)을 조사분석(調査分析)한 결과(結果)는 다음과 같다. 측구침식(側溝浸蝕)에 의한 피해(被害)길이는 전림도(全林道) 연장(10km)의 3%에 해당하였으며, 대부분(大部分) 요형사면(凹型斜面)에 사면장(斜面長) 10m 이상(以上)으로 성토(盛土)된 곡선부(曲線部)에서 발생하였고, 부분적(部分的)으로 상수(常水)가 흐르는 계곡부(溪谷部)에 성토(盛土)된 구역(區域)과 상수(常水)가 있는 배수관(排水管)의 유출구(流出口) 양사면(兩斜面)에 성토(盛土)된 부위에서 붕괴(崩壞)가 많이 발생하였다. 측구침식(側溝浸蝕)의 경우 심한 피해(被害)는 계곡수(溪谷水)가 월수(越水)하여 V형(型) 측구(側溝)를 따라 흐르므로서 피해(被害)를 발생시켰으며, 기타 원인(原因)으로는 종단(縱斷)물매가 10% 이상(以上) 급(急)하게 시공(施工)된 지역(地域)에서 나타나 문제점(問題點)으로 인식되고, 직경(直經) 400mm 이하(以下)인 배수관(排水管)이 매설된 집수정(集水井)이 낙엽(落葉) 등(等)의 퇴적(堆積)으로 매몰된 경우와 경사가 급한 침사지(沈砂池)(집수승(集水桝)) 벽이 무너져 내린 결과 이 지점을 월수(越水)하여 측구침식(側溝浸蝕)을 일으키고 있다. 이상(以上)의 결과(結果)에서 시범임도(示範林道)의 태풍피해(颱風被害)는 임도피해예방(林道被害豫防)을 위한 경험부족(經驗不足)에서 나타낸 현상으로 보인다. 상기(上記)와 같은 점을 개선하면 동(同) 시범임도(示範林道) 조성방법(造成方法)은 경제적(經濟的) 임도(林道)차 모델로서 발달될 수 있을 것이다.

• 한국환경복원기술학회지
• /
• 제18권3호
• /
• pp.13-22
• /
• 2015

Unpaved forest roads are common accessways in mountain areas being used for forestry purposes. The presence of forest roads produces large volumes of surface runoff and sediment yield due to changes in soil properties and hillslope profile. Rainfall simulation experiments were conducted to estimate the impacts of above-ground vegetation and antecedent soil water condition on hydrology and sediment processes. A total of 9 small plots($1m{\times}0.5m$) were installed to represent different road surface conditions: no-vegetation(3 plots), vegetated surface(3 plots), and cleared vegetation surface(3 plots). Experiments were carried out on dry, wet, and very wet soil moisture conditions for each plot. Above ground parts of vegetation on road surface influenced significantly on surface runoff. Runoff from no-vegetation roads(39.24L) was greater than that from vegetated(25.05L), while cleared-vegetation condition is similar to no-vegetation roads(39.72L). Runoff rate responded in a similar way to runoff volume. Soil erosion was also controlled by land cover, but the magnitude is little than that of surface runoff. Even though slight differences among antecedent soil moisture conditions were found on both runoff and soil erosion, runoff rate and soil losses were increased in very wet condition, followed by wet condition. The experiments suggest that vegetation cover on forest road surface seems most effective way to reduce surface runoff and soil erosion during storm periods.

• 한국산림과학회지
• /
• 제102권1호
• /
• pp.30-37
• /
• 2013

이 연구는 식생기반재 돌망태의 침식억지효과 및 녹화효과를 분석하는데 있다. 이 연구를 통하여 얻은 결론은 다음과 같다. 조사기간 중 평균침식량을 분석해 본 결과, 침식량이 가장 많은 순으로 보면 곡선부에서의 일반돌망태시공지(5,840 $cm^3$)>대조구(5,833 $cm^3$)>직선부의 일반돌망태 시공지(5,621 $cm^3$)>곡선부의 식생기반재돌망태시공지(4,298 $cm^3$)> 직선부의 식생기반재돌망태시공지(4,117 $cm^3$)의 순으로 나타나 식생기반재 돌망태를 시공한 것이 임도절토비탈면의 침식을 저감하는데 효과적인 것으로 분석되었다. 아울러 임도 곡선부의 식생기반재돌망태 및 일반돌망태시공지의 토양침식억지효과가 직선부보다 낮게 나타나 이러한 구조물은 곡선부보다는 직선부에 설치하는 것이 효과적일 것으로 사료된다. 조사기간 중 평균식생피복률은 곡선부에서 45(28~65)%로 나타나 동일한 기간 직선부 식생기반재돌망태시공지의 평균피복률 56(30~85)% 보다 약 11(2~20)% 낮은 값을 나타내어 직선부에서의 식생피복률이 높게 나타났다. 또한 임도절토비탈면에 시공한 식생기반재돌망태는 안정화된 이후 임도 절토 비탈면의 토양침식을 억지하는 효과로 인해 식생피복률이 증가하는데 기여하는 것으로 분석되었다.

• 농업생명과학연구
• /
• 제43권4호
• /
• pp.1-8
• /
• 2009

The physically based model KINEROS2 was applied to forest road segments for simulating hydrology and sediment production. Data on rainfall amounts, runoff volume, and sediment yields were collected at two small plots in the Yangpyong experimental watershed. The KlNEROS2 model can be parameterized to match the volume of surface flow and sediment yields during seven storm events. Model predictions of hydrology were in good agreement with the observed data at two plots in the year 1997 and 1998. A comparison between the observed and predicted sediment yields indicated that the model provided reasonable estimates, although the model tended to under-estimate for some storm events. The overall result shows that the KINEROS2 model properly represents the hydrology and sediment transport processes in the forest road segments.

• 한국산림과학회지
• /
• 제89권3호
• /
• pp.397-404
• /
• 2000

임도 옆도랑침식에 영향을 미치는 요인의 평가 및 안정도 판별을 위하여 광릉시험림의 임도를 대상으로 조사를 실시한 결과 침식에 미치는 기여순위는 종단물매, 시설위치, 절토사면경사, 절토사면구성물질, 유하거리, 노면형태, 노면재료, 절토사면피복도, 절토사면길이 순으로 나타났다. 임도 옆도랑침식을 유발하는 요인을 평가하면, 종단물매는 8% 이상, 임도시설위치는 산록(山麓)과 중복(中腹), 절토사면경사는 $50^{\circ}$ 이상, 절토사면토성은 견질토사, 자갈섞인 토사, 호박돌섞인 토사, 유하거리는 80m 이상의 지역에서, 그리고 노면재료는 토사도(土砂道)와 자갈부설도에서, 노면형태의 경우에는 철(凸)형과 직선형, 절토사면 피복도(被覆度)는 피복도가 중(中)이상인 곳에서 임도 옆도랑침식이 발생할 가능성이 높은 것으로 예측(豫測)되었다.