• 한국농공학회논문집
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• 제59권6호
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• pp.109-125
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• 2017

This study aimed to develop a parcel-unit soil loss estimation tool embedded in Excel worksheet, USLExls, required for the design of contaminated farmland restoration project and to analyze the impact of the project carried out soil-filling work on soil loss. USLE method was adopted for the estimation of average annual soil loss in a parcel unit, and each erosivity factor in the USLE equation was defined through the review of previous studies. USLExls was implemented to allow an engineer to try out different combinations just by selecting one among the popular formulas by each factor at a combo box and to simply update parameters by using look-up tables. This study applied it to the estimation of soil loss before and after soil-filling work at Dong-a project area. The average annual soil loss after the project increased by about 2.4 times than before on average, and about 60 % of 291 parcels shifted to worse classes under the classification criteria proposed by Kwak (2005). Although average farmland steepness was lower thanks to land grading work, the soil loss increased because the inappropriate texture of the cover soil induced the soil erosion factor K to increase from 0.33 before to 0.78 after the soil-filling work. The results showed that the selection of cover soil for soil-filling work should be carefully considered in terms soil loss control and the estimation of change in soil loss should be mandatory in planning a contaminated farmland restoration project.

• Journal of the Korean Wood Science and Technology
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• 제2권3호
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• pp.39-41
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• 1974

Bastard indigo, prevailing shrub species planted in erosion control work to constitute vegetation, is proved to be usefull for pulp material other than existing usage of green manure or fuel. Pulp made from bastard indigo is good enough for filler pulp though the quality of it is not remarkably excellent. (1) Sorts of paper possible to make from this pulp. Packing paper of medium grade. (general packing paper except heavy packing) (2) Traits of this pulp as for pulp material (A) It is more preferable than annual plants in these respects, ego collection, transport and storage of pulp material, and yield, freeness and chemical consumption of pulp. (B) Annual probable production of pulp material per ha from this plant is higher than that from long-term tree species or similar to that from fast growing species. (C) Its cultivation on eroded area is welcomed and consecutive annual production of material by copice method is also proved possible.

• 한국산림과학회지
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• 제79권3호
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• pp.269-277
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• 1990

황폐계류(荒廢溪流)에서 발생하고 있는 토사재해(土砂災害)의 방재대책(防災對策)을 수립할 경우 우선 검토되어야 할 것은 하상면(河床面)의 미지형변화(微地形變化)와 사방시설(砂防施設)에 의해 기대되는 하도고정(河道固定)을 예측하는 것이다. 이를 위해 실지계류(溪流)에서 발생되고 있는 하상미지형(河床微地形)의 특성과 사방시설(砂防施設)의 배치효과를 파악하고, 이어서 모형실험(模型實驗)에 의해 그 유효성을 확인하여 저(低)댐의 군적(群的)배치에 의한 하상미지형(河床微地形)의 변화에 대하여 검토하였다. 실험결과에서 저(低)댐의 군적(群的)배치가 하도고정(河道固定)에 미치는 영향은 국소세굴(局所洗掘) 방지, 유로폭(流路幅)과 퇴적역(堆積域)의 확대였다. 1. 저(低)댐 군(郡)의 배치(L'/L=1)에 의해 국소세굴(局所洗掘)을 일으키는 유수(流水)의 편류현상(偏流現象)에 대하여 댐이 유수(流水)와 토사(土砂)를 분리하여 퇴적(堆積)을 촉진시킴과 동시에 유하수(流下水)를 분산시켜 소유력(掃流力)을 감소시켰다. 따라서 횡단면변동량(橫斷面變動量)(F.A.)은 무시설(無施設)시에 비하여 약65%가 저감(低減)되었다. 2. 유로폭(流路幅)에 대한 저(低)댐군(郡)의 배치효과는 사방시설(砂防施設)의 시공구간장(施工區間長)에 비례하여 증가되었다. 전 구간에 사방시설(砂防施設)을 배치하였을 경우(L'/L=1)는 무시설(無施設)시 (L'/L=0)에 비해 1.53배 확보되었다. 3. 하도내(河道內)에 이종토사(移種土砂)가 퇴적(堆積)하기 위하여는 퇴적공간(堆積空間)이 필요하며, 퇴적토사(堆積土砂)가 안정하는 조건으로 소유력(掃流力)이 감소와 함께 퇴적역(堆積域)의 확보가 필요하다. 저(低)댐군(郡)의 배치에 의해 퇴적역(堆積域)은 약 2.10배 증가하였다.

• 환경영향평가
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• 제26권6호
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• pp.457-469
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• 2017

개발사업 예정지역에서 토양의 본래 기능을 최대한 보전하기 위해 토양을 중점적으로 관리하는 지역(토양중점관리지역)을 선정하여 관리할 필요가 있다. 이에 본 연구에서는 개발사업 환경영향평가시 어떻게 토양중점관리지역을 선정할 것인지에 대한 예비연구를 수행하였다. 토양 기능중 토양침식조절기능과 토양탄소저장기능을 우선적으로 고려하여 InVEST 모형을 활용한 정량적 평가를 수행하였고 중첩분석을 통해 2개의 개발사업 사례에 대해 토양중점관리지역을 선정하였다. 본 연구를 통해 개발된 방법론은 고해상도의 정밀한 분석, 다른 평가항목들과의 중첩분석 등 다양하게 활용할 수 있다. 좀 더 완벽한 평가를 위해 토양의 다양한 기능을 포함한 평가방법론을 개발할 필요가 있다.

• 한국환경복원기술학회지
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• 제1권1호
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• pp.28-44
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• 1998

This study was conducted to suggest the ecological restoration strategies for the disturbed landscapes by theoretical study. Especially, it is aimed to suggest three objectives for restoration by using native plants ; (1) prevention or reduction of wind and water erosion, (2) provision of food and cover for variety of animal species, (3) improvement of the visual or aesthetic quality of disturbed sites. The main results were summarized as follows. 1. Cooperation between restoration ecologists and restoration practitioners is needed to delineate a scientific approach to restoration ; (1) Being aware of published literature that describes similar work and/or establish general principles. (2) Preparedness to carry out proper experiments to test ideas. (3) Preparedness to monitor fundamental parameters in a restoration scheme. (4) Providing information about the behavior of species. (5) Publish results. 2. There are three models of succession in theories of plant succession. The tolerance and facilitation models were recommended to ecological restoration. The inhibition model applies in most secondary succession, but the actual species which are introduced first may inhibit the germination and growth of slower-growing species, or they may prevent the growth of other species whose propagules arrive later. 3. The objectives of erosion control, wildlife habitat provision, and visual quality improvement are not mutually exclusive. However, many revegetation practices in the past have emphasized one of these aspects at the expense of the others. 4. A native plant community can be the model of ecological restoration. By stylization/abstraction of native plant community, trying to learn the most essential characteristics of community types - environmental factors ; dominant, prevalent, and "visual essence" species composition - in order to use such information in restoration. 5. After developing mass/spaces plan, match plant communities to the mass/space plan. In utilizing community grouping, there needs aesthetic ability to understand design elements. 6. Several hydrophytes such as Pennisetum saccharifluous, Themeda triandra, Cirsium pendulum show relatively good germination rates. In case of mesophytes and xerophytes, Arundinella hina, Artemisia princeps, Oenothera odorata and legumes seem to have quick-germinating abilities at barren sites. Pinus thunbergii, Rhus chinensis, Evodia daniellii, Alnus firma and Albizzia julibrissin can be considered as "late succession" woody plants because they show low germinating rates and slow growing habitat. 7. The seeds used for restoration should be collected within a certain radius of where it will be planted. Consideration in genetic issues in the collection and use of germplasm can increase the odds for successful restoration efforts. 8. The useful model in the "drift" pattern occurs so abundantly in naturally evolving landscapes. As one species diminishes in density, a second or third species are increased. Thus, dynamic interactions between species are created. Careful using of "drift phenomenon" in planting was recommended. 9. Virtually no stand of vegetation today is immune from the introduction and/or spreading of exotic species. Therefore, the perpetuation of a restored sites requires conscious monitoring and management. Thus, management would be the most important process in ecological restoration. 10. In order to keep the sites "natural", alternative management strategies would be applied in management ; Atenative management strategies are decelerating successional process, accelerating successional processes or modifying species composition. As management tools, mechanical, chemical, biological or environmental factor manipulation, e.g., fire could be used.

• 한국산림과학회지
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• 제105권3호
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• pp.321-329
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• 2016

이 연구에서는 2006년 집중호우 시 산사태 및 토석류가 발생한 강원도 인제군의 기룡산 유역을 대상으로 사면붕괴 및 계상변동을 추정하여 만사 상태에 도달한 불투과형 사방댐이 토사유출 조절에 미치는 영향을 정량적으로 해석하고, 이를 토대로 사방댐의 설계 및 준설기준을 고도화하는 데에 필요한 새로운 인자를 제안하였다. 일반적으로 사방댐은 계획평형기울기 구간과 계획홍수기울기 구간에서 각각 토사유출의 억제와 조절 기능을 발휘하고 있다. 연구대상유역에 시공된 불투과형 사방댐은 계획억제토사량에 해당하는 저사량이 $2,111m^3$로 설계되었지만, 2006년 집중호우로 인한 산지교란 발생 시에는 해당 사방댐 직상부로부터 250 m의 계류구간에 걸쳐 $3,996m^3$의 유출토사를 조절한 것으로 관측되었다. 결과적으로 해당 사방댐은 유출토사 억제를 위한 계획억제토사량보다 큰 규모의 계획조절토사량을 나타내어 만사된 이후에도 유출토사의 조절이라는 사방댐의 기능을 발휘하고 있었다. 이와 같이 사방댐의 토사유출 조절기능은 토사유출 억제기능과 구분하여 평가하여야 하지만, 현재 우리나라에서는 현지에서 유역 특성을 실측한 자료를 기반으로 한 계획억제토사량 또는 계획조절토사량을 사방댐의 설계 및 준설기준 인자로서 고려하고 있지 않다. 따라서 합리적인 사방댐의 설계 및 유지관리 기준을 마련하기 위해서는 사방댐의 토사유출 억제기능과 조절기능을 정량적으로 해석한 현장자료가 축적되어야 하며, 이는 우리의 사방기술이 보다 객관적이고도 체계적인 면모를 갖춘 과학적 기술로 발전할 수 있는 방안일 것이다.

• 한국환경복원기술학회지
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• 제6권6호
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• pp.56-71
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• 2003

Waste landfills have been the center of environmental problems and they must be restored due to environmental pollution, disgusting landscape, and cost of management. It is suggested that they be recycled urban space as cities expand. Specially, nonsanitary waste landfills which have no pollution prevention facilities cause serious problems. Restoring the landfills as parks and golf courses, so on makes more benefits because of cheap use land, closeness to urban area, flat topography applicable to parks and golf courses, and high land values after restoration and the changes to local recreation sites. Restoration of waste landfills is a complex, costly, and interdisciplinary work. But, the waste landfill is a manmade ecosystem. Control, restoration and postmanagement of waste landfills are very important problems. The role of vegetation prevents soil erosion, reduces soil water storage, and obstructs leachate seepage. Early restoration makes derelict lands into man park artificially geared to soil, vegetation, landforms and hydrology. But, Ideal restoration is to make stable ecosystem nature-friendly and compatible with surrounding landscape without more management. Landscape is structured hierarchically with patches and stands as small components and forms forest as large components. Therefore, landscape formation of the waste landfills needs much restoration process. There are many ecological restoration techniques for the waste landfills. Those are divided into artificial and natural methods. The artificial method is anthropogenic plantings while the natural method is to trigger and use succession processes. The most important thing in the restoration of waste landfills is to consider the final restoration objectives of each waste landfill. According to these objectives, the depth of covering layer, planting degree, and structural design should be determined. The effective restoration methods should be selected of artificial and natural options.

• 한국재난정보학회 논문집
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• 제17권4호
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• pp.694-709
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• 2021

연구목적: 지진에 의한 산사태 위험도 평가를 통하여 지진발생 전에는 산사태 예방사업, 지진발생 후에는 피해지 예측 및 복구 우선순위 선정으로 지진유발 산사태 피해저감을 효율적·선제적으로 하기 위한 기초자료를 제공하고자 수행하였다. 연구방법: 국외 선행연구를 분석하여 평가 방법론 검토와 평가 인자를 도출하고 국내 산사태 위험지도 활용성을 검토하였다. 또한 지진동 감쇠식을 이용하여 포항지역의 단층대 및 진앙지 기준으로 지진에 의한 산사태 위험지도를 시범 구축하였다. 연구결과: 지진에 의한 산사태 위험도 평가 연구는 중국이 전체의 44%, 이탈리아 16%, 미국 15%, 일본 10%, 대만 8% 순으로 나타났다. 평가 방법론으로 통계적 모형이 59%로 가장 많았고, 물리적 모형이 23%로 나타났다. 통계적 모형에 많이 사용된 인자는 고도, 단층대와의 거리, 경사도, 사면방향, 모암, 지형곡률로 나타났다. 현재 국내의 산사태 위험지도는 지형·지질·임상이 반영되는데 이를 활용한 지진에 의한 산사태 위험도 평가는 합리적인 것으로 나타났다. 포항지역에 단층대 및 진앙지 기준으로 산사태 위험도를 평가한 결과 기존의 낮은 등급이 높은 등급으로 변화하는 등 지진의 영향이 고려되었다. 결론: 광역 단위의 지진유발 산사태 위험도 평가를 위해서는 산사태 위험지도를 활용하는 것이 효율적이다. 단층대 기준의 위험지도는 지진에 의한 산사태 피해방지를 위한 예방사방사업 대상지 선정에 활용하고, 진앙지 기준의 위험지도는 지진이 발생한 이후 산사태 피해 현황을 조사하거나 피해지 복구 등 피해방지 대책 우선순위 선정의 효율적 사후관리에 활용할 수 있다.

• 환경영향평가
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• 제16권2호
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• pp.143-156
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• 2007

This study has researched the management status and the pollution level of water, soil, stream sediments of 11 abandoned coal mines out of a total of 12 within Obong-Dam area except Bukyung mine, which was submerged when constructing Obong-Dam, and selected areas which are in needs to have pollution control facilities in the first place. From the results of examination on the runoff at the waste rock pile and mineheads, the runoff from Sueun mine (pH, Fe, Al), Samwon mine (pH, Al), Wangdo mine (pH, Al), Mose mine (pH, Fe, Al) and Daeryeong mine (pH) exceeded the permissible discharge standards of the water quality, but the water at merging point with Obong-Dam after joined with Doma branch satisfied both Water Quality Standards and Drinking Water Quality Standards. In regard to groundwater contamination, it is found that areas where exceeded the Drinking Water Quality Standards are Wangdo mine (pH), Jangjae mine (pH, Zn), Daeryeong mine (pH) whereas all areas satisfied Soil Contamination Warning Standards of Soil Environmental Conservation Law. When comparing a research result on underwater sediments of branches of abandoned mines to the EPA Guidelines for classification of great lakes harbor sediments, Dongguk Gaerim (Fe), Jungwon mine (Fe), Daebo mine (Mn), Samwon mine (Mn) and Daeryeong mine (Mn) showed mid-level of contamination, whereas Sueun (Fe, Mn), Daebo mine (Fe), Woosung mine (Fe, Mn), Wangdo mine (Fe, Mn), Mose mine (Fe) and Daeryeong mine (Fe) showed high-level of contamination. In addition, contamination levels of underwater sediments in Wangsan and Doma branch where abandoned mine's branches merge together, Wangsan branch showed no contamination at all whereas Doma branch shows mid-level of contamination which reflect the Doma branch is affected by waste rock pile and minehead runoff of the abandoned mines in the Doma branch area. It is concluded that Mose mine and Sueun mine required treatment of acid mine drainage. and Wangdo, Jungwon, and Samwon mines were in need of mine tailing and erosion control work. The Samwon mine additionally required a control system for closed minehead runoff. Although the Samwon mine reached a high concentration of Al, Mn $Ca^{2+}$, $SO{_4}^{2-}$ in the runoff, the levels decreased after it was combined with a tributary. It has been concluded that after further monitoring of the cause of pollution, a preventive measure system may be needed to be built.

• 한국환경복원기술학회지
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• 제3권2호
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• pp.24-34
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• 2000

The project for rehabilitation and revegetation of the abandoned coal-mine lands is a very important national environmental restoration project in the view point of rehabilitation and revegetation of denuded forest-lands caused by coal mining as well as restoration of disturbed natural environment and control of the variable pollutions. In Korea, because a large number of coal mines had been developed in order to fill up abundantly consumption of coal as a major energy source in the developing period, a lot of denuded forest-lands caused by coal mining had distributed in the whole country. And, due to the absence of effective rehabilitation and revegetation works on the denuded forestlands caused by coal-mining, most of them had been remained with being damaged. In 1990, area of the abandoned coal-mine lands, requiring the rehabilitation and revegetation works, was about 1,437.1 ha. For the past ten years ('90~'99), about 1,081.8 ha out of them had been rehabilitated and revegetated, and the rehabilitation planning area was about 33.0 ha in 2000. So, remaining area out of abandoned coal-mine lands will be about 322.3 ha after 2000. In principle, after abandoning coal-mine, mine owners must carry out the rehabilitation and revegetation works on the abandoned mine lands by themselves. But, most of mine owners were in financial difficulty after abandoning coal-mine, so that principle couldn't have obtained the desired effects. To solve this problem, from 1995, Coal Industry Promotion Board (CIPB) have carried out the rehabilitation and revegetation works on the abandoned coal-mine lands at government budgets, and they have obtained good results in the construction area. However, due to application of the "conventional erosion control measures and techniques" to the rehabilitation and revegetation measures on the abandoned coal-mine lands, the results and effects of the works excuted have not been successful. Therefore, unique measures and techniques for rehabilitation and revegetation of the abandoned coal-mine lands will have to be developed, especially including development of new techniques on the soil-dressing and soil-covering, seed spray and hydro-seeding measures with seed-fertilizer-soil materials as the mechanized measures, and using of new materials for the tree planting and seedling measures.