• 한국환경복원기술학회지
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• 제7권2호
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• pp.87-95
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• 2004

For the slope stability and revegetation of retaining wall, Eco-Stone was built beside a newly constructed road in August, 2002. Eco-Stone blocks were constructed in 4 different combinations of irrigation and soil types. Within the Eco-Stone, planted were 6 species such as Forsythia koreana, Rhododendron mucronulatum, Spiraea prunifolia var. simpliciflora, Rhododendron sp. Euonymus japonica, and Aster koraiensis. Shoot growth was greater on common soils than at a better soil treatment for Forsythia koreana(P<0.01) and Spiraea prunifolia var. simpliciflora(P<0.05), while there were no significant differences for the other species. Biomass increment of the planted species also did not show significant differences between irrigation types, except Rhododendron sp. and Aster koraiensis of which biomass was higher under irrigation than at no irrigation for common soils. Most of the planted individuals were alive, showing survival ratio of 90~97% with no significant differences among treatment blocks. These results imply that the Eco-Stone can be used economically for slope stability and revegetation instead of concrete blocks, without a specific soil and irrigation requirement.

• 한국산림과학회지
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• 제105권4호
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• pp.449-455
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• 2016

본 연구는 임도사업의 계획과 유지관리 단계에서 임도 관리자 집단의 의식성향을 파악하여 체계적인 임도 정책 수립을 위한 기초자료를 제공하기 위하여 수행하였다. 임도의 계획과 유지관리에 대한 설문조사 결과, 임도 노선의 계획시 고려사항으로는 육림작업, 산지재해 예방, 목재수확 등의 항목에서 높은 중요도를 보였으며, 간선임도에 대한 선호도가 가장 높게 나타났다. 또한 임도 유지관리 작업의 적절성에 대해서는 두 집단 모두 인력 및 예산부족으로 인한 어려움(92.9%)이 있다고 응답하였다. 임도의 개설로 우려되는 주요 피해형태로는 사면붕괴로 인한 인명피해, 사유지 통행에 대한 분쟁 등의 순으로 나타났으며, 현재 실행하고 있는 임도 유지 관리작업의 주요 내용으로는 배수시설의 정비와 노면정비가 높게 나타났다. 임도시설에 대한 주요 보완사항으로는 배수시설, 비탈면 녹화와 안정에 대한 응답이 높게 나타났다.

• 한국환경복원기술학회지
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• 제21권4호
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• pp.75-86
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• 2018

This research was thereby made to study and analysis ecological, landscape, and stability qualities of roadside cut Slopes in expressways and national highways that went through revegetation works. Also, evaluation items and framework for integrated assessment of plant structure and restored state for the maintenance were suggested. Following is the summary of the result. firstly, for stabilization of introduced native plant species on roadside cut slops, assessment on the post-project environmental management through long-term monitoring and maintenance works must be made. It signifies a form of authentic recovery and restoration by the native plants. second, current evaluation framework on the test beds is well managed with clear evaluation standards and table while its method of assessing the post management with only test bed results lacks conformity with this study site. Newly developed evaluation framework on the post construction sites is estimated to be used as assessment standards on any roadside construction sites. Third, after site investigation distinction was observed among different revegetating construction types in the long-term perspective. Due to the different duration time of vegetation state between seed-spray measures(degraded in time) and layer-spray measure(maintained), the use of coarse straw-mat mulching work or Coir net was suggested in long term maintenance of cut slopes. forth, segmentation of post environmental assessment is organized into three large categories of "ecological", "stabile", and "landscape" qualities regarding post restoration quality and stability of slope through native plants with which categories marks 50, 30, 20 points of rates. fifth, components of the post environmental assessment were segmented in twelve categories driving results from former experimental construction and newly focused items on site. In the future, it is possible to propose a customized assessment method considering the location and location of construction work if the research on the application of post-environment assessment methods for road construction surface recording is conducted systematically.

• 한국환경복원기술학회지
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• 제10권2호
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• pp.1-15
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• 2007

A variety of revegetation methods are being utilized and developed. However, most of revegetation methods used on highway slopes in Korea are based on foreign-introduced plant varieties to stabilize road surfaces and to administer afforestation for surface covering at an earlier phase. Therefore. it results in various problems. such as failure to achieve harmony with the surrounding vegetation and 10 cause re-denudation of slopes as the foreign-in introduced plant varieties wane out from 2~3 years after hydro-seeding, etc. In addition, some of the revegetation plants seeded in the earlier phase grow excessively high, thus causes successional problems, such as to inhibit the invasion of the secondary vegetation from the surrounding areas, etc. Therefore, in this study, 160 slopes located in the nationwide express highways have been investigated and analyzed in order to produce basic data for restoration of ecological environment in slopes created on a long-term basis by investigating and analyzing locational characteristics of cut and filled slopes in express highways, status of revegetation methods, characteristics of soil and plant-ecological environment. 1. Investigation on cut and embanked slopes in express highways was carried out in the total of 160 locations, which include 108 cut slopes and 52 embanked slopes. As a whole, the most frequently used revegetation method was seed spray, which was found to be used in the total of 55 target slops investigated. 2. Planting method of Wistaria floribunda applied to some of the blasted rock zones was found to cause damages as Wistaria floribunda trailed up the surrounding vegetation and the secondary invaded trees. In order to prevent this, this method must be used only in the lowest parts of large-sized slopes. Also, it will be required to administer continuous management and maintenance in the areas already planted with this plants. 3. The areas of blasted rock and ripping rock slopes were applied with coir net (net + seeding) method. However, many of these areas failed in achieving ground covering. Most areas where revegetation was in progress, they were covered with Eragrostis curvula(Weeping lovegrass) only. In areas with soil, such as decomposition of granite, where afforestation is difficult. In this slopes, soil base must be improved by hrdroseeding with thin-layer vegetation base application methods in order to achieve success in afforestation with native plants. 4. Woody species, rather than herb species, are more helpful in stabilization of slope surfaces. Therefore, it is important to be able to grow and protect woody species on highway slopes. Growth of woody vegetation is most largely influenced by soil depth. Thus, when hydro-seeding woody plants, it is recommended to apply at the upper layer of the slopes, which is capable to sufficiently provide the fundamentals required in plant growth.

• 한국조경학회지
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• 제23권2호
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• pp.113-123
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• 1995

This study was conducted to find out appropriate rates of seed mixture of both native and foreign plants in order for stabilization of early afforestation and proper vegetation on road slope. The results are summarized as follows: 1. Characteristics of germination : After seeding, 2 weeks for both Lespedeza bicolor and Lespedeza cuneata, and 4 weeks for both Arundinella hirta and Zoysia japonica were needed for vigorous germination, and 1-4 wee17s for 3 cool-season grasses were spent for gradual germination. 2. Plant height : There was no difference between Lespedeza cuneata and Lespedeza bicolor in plant height by 7 treatments. As mixture rates of cool-season grasses were lowered, plant height of Arundinella hirta became longer. Descending order of co81-season grasses for plant height was Tall fescue, Perennial ryegrass and Creeping redfescue. 3. Number of tillers : The number of tillers tended to increase in the experimental plots where competition was low. 4 Ground cover rate : Ground cover rate was the highest in Mixture IV (96.7%) and was fluctuated from 13.3% on Sept. 13 to 45% on Nev. 3 in Mixture III. Descending order of gronud cover rates in 7 treaments was Mixture IV, Mixture III. Mixture II, Mixture Ⅶ, Mixture V, Mixture Ⅵ, Mixture I, and Mixtur III when measured on Oct. 13 5. Visual assessment: High preferences were observed on Mixture IV and Ⅶ In sun the best seed mixtures were Mixture IV and Ⅶ. It meant that (1) either mixture of 70% the native plants with 30% cool-season graaes or (2) mixture of 80% the native plants with 20% cool-season glasses was best for this study.

• 한국산림과학회지
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• 제84권2호
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• pp.239-246
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• 1995

이 연구(硏究)는 대규모(大規模) 벌채지(伐採地) 운재로(運材路)에서의 침식(浸蝕) 및 퇴적(堆積)에 관련되는 주요(主要) 인자(因子)와 그 영향(影響)을 구명(究明)할 목적(目的)으로 1993년부터 1994년까지 2개년간 백운산(白雲山) 지역(地域)(서울대학교(大學校) 농업생명과학대학(農業生命科學大學) 부속(附屬) 남부연습림(南部演習林) 제(第)26임반(林班)에 개설된 운재로(運材路)에서 수행한 연구(硏究)로서 결과(結果)를 요약(要約)하면 다음과 같다. 1. 운재로(運材路) 노면(路面) 침식(浸蝕)의 설명에 유의한 인자(因子)는 누가강우량(累加降雨量), 침식거리(浸蝕距離), 운재로(運材路)의 횡단(橫斷)물매, 토양경도(土壤硬度) 등(等) 4개(個) 인자(因子)이었으며, 누가강우량(累加降雨量)이 많을수록, 운재로(運材路) 시점(始點)으로부터 거리가 멀수록, 운재로(運材路)의 횡단(橫斷)물매가 급할수록 운재로(運材路)의 노면(路面) 침식량(浸蝕量)은 증가하였다. 2. 우재로(運材路)에서 절토사면(切土斜面) 침식량(浸蝕量)의 설명(說明)에 유의한 인자(因子)는 절토사면(切土斜面)의 모양(模樣), 침식(浸蝕)편의 위치(位置), 식생피복도(植生被覆度), 토양경도(土壤硬度), 모래함유율(含有率), 누가강우량(累加降雨量), 점토함유율(粘土含有率), 미사함유율(含有率) 등(等) 8개(個) 인자(因子)이었으며, 식생피복도(植生被覆度)가 낮을수록, 누가강우량(累加降雨量)이 많을수록, 토양중(土壤中)의 모래함유율(含有率)이 많을수록 운재로(運材路)의 절토사면(切土斜面) 침식량(浸蝕量)은 증가하였다. 3. 운재로(運材路)에서 발생된 총침식량(總浸蝕量)의 설명에 유의한 인자(因子)는 총강우량(總降雨量), 강우(降雨)횟수, 토양경도(土壤硬度) 등(等) 3개(個) 인자(因子)이었으며, 강우량(降雨量)이 많을수록, 강우(降雨)횟수가 많을수록 운재로(運材路)의 성토사면(盛土斜面) 침식량(浸蝕量)은 증가하였다. 4. 운재로(運材路)d서 발생된 총침식량(總浸蝕量)은 운재로(運材路) 개설(開設) 당해연도(當該年度)에는 $5.04{\times}10^{-2}m^2/m^2$, 그 다음 해에는 $7.37{\times}10^{-2}m^2/m^2$로, 이중 노면(路面) 침식량(浸蝕量)은 운재로(運材路) 개설(開設) 당해연도(當該年度)와 그 다음 해에 각각 운재로(運材路) 총침식량(總浸蝕量)의 32.7%, 57.1%, 절토사면(切土斜面) 침식량(浸蝕量)은 각각 총침식량(總浸蝕量)의 30.4%, 21.0%, 성토사면(盛土斜面) 침식량(浸蝕量)은 각각 총침식량(總浸蝕量)의 36.9%, 21.9%이었다. 이상(以上)의 결과(結果)를 종합해 볼 때 산림벌채(山林伐採)를 위하여 개설(開設)된 운재로(運材路)에서 침식(浸蝕)을 저감(低減)하기 위해서는 운재로(運材路) 개설시(開設時) 환경보전적(環境保全的)으로 적절한 노선(路線) 설계(設計)가 이루어져야 하며, 절 성토사면(切 盛土斜面)에는 조기(早期) 식생피복(植生被覆)을 위한 안정(安定) 녹화(綠化) 방안(方案)이 강구되어야 할 것이다.

• 한국산림과학회지
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• 제96권6호
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• pp.652-660
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• 2007

1989년부터 2005년까지 시공된 전라북도 내의 민유임도 216개 노선의 설계도서를 대상으로 임도 설계상의 주요 공종변화를 분석하였다. 전라북도의 연평균 민유임도 시설거리는 녹색임도 정책 시행 이전단계에 비해 녹색임도 정책 시행 이후 대폭 감소하였다. 토사절취작업은 1990년부터 블도저에서 블도저와 굴삭기 혼용으로 바뀌었다. 비탈면 녹화공은 초기에는 잔디심기와 족제비싸리심기가 주종을 이루었는데, 녹색임도정책 시행단계(2단계)부터 종자뿜어붙이기와 줄파종의 혼용, Coir net 또는 볏짚거적 덮기 등으로 발전하였다. 횡단배수관의 경우, 배수관의 설치 간격은 3단계에 평균 92 m로 감소하였고, 규격은 2단계 이후에 대부분 600 mm 이상으로 확대되었으며, 재료는 모두 파형강관으로 설계되었다. 콘크리트포장은 1단계의 평균 40 m/km에서 3단계에는 240 m/km로 현저히 증가하여 임도의 안정성과 기능성이 제고되었다. 비탈안정구조물은 석축이 주종을 이루고 있지만, 1993년 이후부터 콘크리트옹벽과 돌망태옹벽 등도 많이 설계되었다. 이와 같은 분석을 바탕으로 본 연구에서는 주요 공종을 대상으로 몇 가지 개선방안을 제안하였다.

• 한국산림과학회지
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• 제83권4호
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• pp.545-555
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• 1994

이 연구(硏究)는 벌채작업후(伐採作業後) 방치된 운재로의 조기식생회복(早期植生回復)을 위한 과학적(科學的)인 기초자료(基礎資料)를 제공할 목적(目的)으로 1989년(年)부터 1994년(年)까지 서울대학교(大學校) 농업생명과학대학(農業生命科學大學) 부속(附屬) 남부연습림(南部演習林) 백운산지구(白雲山地區) 제(第) 26 임반(林班), 제(第) 27 임반(林班)에 연차적(年次的)으로 개설(開設)된 운재로(運材路)를 대상(對象)으로 이 연구(硏究)를 수행하였다. 운재로(運材路) 노면(路面)의 토양교란(土壤攪亂)으로 인한 토양가밀도(土壤假密度)와 자연식생회복(自然植生回復)을 조사(調査) 분석(分析)한 결과(結果)는 다음과 같다. 운재로(運材路) 노면(路面)의 토양가밀도(土壤假密度)는 운재로 개설후 시간의 경과에 따라 자연임지(自然林地) 상태(狀態)로 회복(回復)되어 가는데 약 10년이 소요되며, 계산식(計算式)은 다음과 같다. $$Y_1=1.4195-0.0744{\cdot}X(R^2=0.91)$$, $$Y_2=1.4673-0.0688{\cdot}X(R^2=0.73)$$ (단, X : 경과년수, $Y_1$ : 토양 0~7.5cm의 가밀도, $Y_2$ : 토양 7.5~15cm의 가밀도) 수림대(樹林帶)를 조성(造成)하고 운재로(運材路)를 개설(開設)한 지역(地域)의 토양깊이별 가밀도(假密度)는 각각 $0.892g/cm^3$, $0.903g/cm^3$로 수림대를 조성하지 않은 운재로보다 약 20% 낮았다. 운재로(運材路) 절(切) 성토사면(盛土斜面), 노면(路面)에 침입하는 목본의 중요도(重要度)는 산딸기, 산벚나무, 참싸리 등의 순이었으며, 초본은 고사리, 새, 큰까치수영 등의 순이었다. 또한 운재로 폐쇄후 약 6년이 경과되었을 때 식생피복도(植生被覆度)는 절(切) 성토사면(盛土斜面)은 약 70%, 노면은 약 20%로 운재로의 폐쇄후 조기에 인공적(人工的)으로 식생회복(植生回復)을 도모하는 방안이 검토되어야 할 것으로 사료된다. 따라서 성숙임목수확(成熟林木收穫) 벌채지역(伐採地域)에서 운재로(運材路) 개설시(開設時)에는 수림대(樹林帶)를 조성하여야 하며, 운재로 사용이 완료된 후에는 녹화수목식재공사(綠化樹木植栽工事) 및 파종공사(播種工事)와 노면굴기작업(路面掘起作業) 등을 통하여 운재로(運材路) 노면(路面) 토양(土壤)의 조속(早速)한 회복(回復)과 식생피복녹화(植生被覆綠化)를 유도하여야 할 것이다.

• 한국환경복원기술학회지
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• 제10권4호
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• pp.70-82
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• 2007

Aiming at nature's early restoring needs to select plant species harmonizing with surrounding environment that fits to restoring goal of ultimately aiming at woody plants dominant vegetation that protect and stabilize surface parts of bared slopes. And it is important to make it assimilated with surrounding natural vegetation by differentiating planning of seed mixtures. Natural Ecological Restoring Construction Methods (JSB Method) was developed to increase the effect of landscape change according to seasons not to simple hydro-seeding by reducing rate of foreign grasses while raising rate of wild flower using. It was considered that using wild flowers that bloom on each season solved the problems of slope landscapes that looks artificial and uninteresting. After researching environmental condition of the slopes, JSB Method has shown that, as of wet-type method, soil is relatively soft and the difference of thickness of plant base soil media affects on the difference of soil hardness. In case of soil hardness of 8.8~17mm, there's dangerousness of slope's collapsing, but it has shown that growth of plant was favorable. For the acidity of soil, most of them are in the type of neutralized soil of more than pH 6. And after analyzing the degree of woody plants dominance, it had shown that lower part was occupied with wild flowers and other herbaceous species like China pin, golden phesant mum, pitcher plant, and middle and upper part was occupied with woody plants like silk-tree, sumac forming multi-layer structure. It can be concluded that the restoration objects of the woody plant vegetation on the roadside slopes can be accomplished successfully by Natural Ecological Restoring Construction Method (JSB method).