• 환경영향평가
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• 제9권3호
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• pp.239-248
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• 2000

The aggravating water quality from the expansion of industrialization along with increasing population lead to develop more intensive physical measures to secure better drinking water quality. This study was mainly initiated to establish a water-pollutant buffering zone for the upper stream basin of Paldang--the major source area of drinking water for the metropolitan Seoul and suburban areas with a population more than 13 million. Two different criteria were considered in determining the buffering distance from the edge of the streamflow : 1km-width buffer zone for the special protection area which has been strictly controlled by the conventional laws for the protection of drinking water supply, and 500m-width buffer zone for the rest of the area. To delineate the exact boundaries of the water-pollutant buffering zone, GIS database was created integrating topography, hydrography, cadastral, and other related layers. The newly designated water-pollutant buffering zone would contribute to improve the water quality in a long term along with the conservation of the wet land. More study, however, should be made within the water-pollutant buffering zone such as the detailed survey of the pollutants, vegetation, and ecosystem for more effective management of the buffering zone.

• 대한원격탐사학회:학술대회논문집
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• 대한원격탐사학회 2002년도 Proceedings of International Symposium on Remote Sensing
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• pp.506-506
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• 2002

S. Korean Government has accelerating its efforts to enhance the quality of the drinking water. The Ministry of Environment has declared the law of securing water-pollutant buffering zone to minimize the inflow of the point and nonpoint sources into the drinking water sources. As a first phase of installing nationa-wide water-pollutant buffering zone, approximately 300km buffering zone has been delineated along the South and North Han river, the major drinking water sources for the capital area of S. Korea, which has the population of more than 12 millions. The buffering zone has the width of 1,000 meter for the special protection area, and 500 meter for the remaining area from both ends of the river. The major works have been done in three stages. Firstly, the boundaries lines of the buffering zone was delineated on the digital topographic maps. Secondly, the maps were overlayed with the cadastral maps to identify individual land parcels, the street address of the major pollutant discharging facilities, and all different types of pollutants including livestocks. Thirdly, the field work has been done as a verification. Once the buffering zone was generated, all the information for the buffering gone were created or imported from other government agencies including official land price, details of the major manufacturing facilities discharging considerable amount of pollutants, major motels and resorts, not to mention of restaurants, etc. Also, major livestock houses were located to identify the path of the pollutant inflow to the drinking water source. Further works need to be continued such as purchasing private lands within the buffering zone and change the land use in the efforts to decrease the pollutant amount and to provide more environmentally friendly space. Also, high resolution satellite imagery should be utilized in the near future as a cost-effective data source to update all the landuse activities within buffering zone.

• 한국수자원학회:학술대회논문집
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• 한국수자원학회 2006년도 학술발표회 논문집
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• pp.908-912
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• 2006

임하호 유역은 지질 및 지형이 토사유실에 취약한 구조를 가지고 있어 강우발생시 많은 토사가 호소로 유입되어 고탁수의 원인이 되고 있다. 특히 임하호유역의 농경지가 주로 하천주변에 분포하고 있어 강우시 토사유실로 인한 탁수발생이 큰 지역이다. 따라서, 탁수저감을 위한 수변구역의 체계적인 관리와 대책 마련을 위해서는 수변구역에서 발생하는 토사유실량의 영향을 평가하는 것이 중요하다. 본 연구에서는 GIS 기반 RUSLE 모형을 선정하여 수변구역에서의 토사유실 비율을 평가한 결과 약 12.23%로서 임하호 전체유역과의 면적비율(9.95%) 보다 높게 나타남을 알 수 있었다. 이러한 결과는 수변구역 주변의 농경지비율(27.24%)이 전체유역에 대한 농경지비율(14.96%) 보다 높은 특성이 반영된 것으로 해석된다. 또한 소유역별 분석결과를 볼 때 수변구역중 대곡천 유역이 가장 높은 토사유실량 분포를 나타냈으며, 반변천_10 그리고 서시천 순서로 나타났다.

• 대한토목학회논문집
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• 제26권2D호
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• pp.335-340
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• 2006

임하호 유역은 지질 및 지형이 토사유실에 취약한 구조를 가지고 있어 강우발생시 많은 토사가 호소로 유입되어 고탁수의 원인이 되고 있다. 특히 임하호유역의 농경지가 주로 하천주변에 분포하고 있어 강우시 토사유실로 인한 탁수발생이 큰 지역이다. 따라서, 탁수저감을 위한 수변구역의 체계적인 관리와 대책 마련을 위해서는 수변구역에서 발생하는 토사유실량의 영향을 평가하는 것이 중요하다. 본 연구에서는 GIS 기반 RUSLE 모형을 선정하여 수변구역에서의 토사유실 비율을 평가한 결과 약 12.23%로서 임하호 전체유역과의 면적비율(9.95%) 보다 높게 나타남을 알 수 있었다. 이러한 결과는 수변구역 주변의 농경지비율(27.24%)이 전체유역에 대한 농경지비율(14.96%) 보다 높은 특성이 반영된 것으로 해석된다. 또한 소유역별 분석결과를 볼 때 수변구역중 대곡천 유역이 가장 높은 토사유실량 분포를 나타냈으며, 반변천_10 그리고 서시천 순서로 나타났다.

• 한국GIS학회:학술대회논문집
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• 한국GIS학회 2002년도 춘계학술대회논문집
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• pp.153-159
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• 2002

This study mainly concentrates on the development of a land information management system to manage the land related information in an effective way for the water-pollutant buffering zone, which was established to sustain better quality of the drinking water over the upper part of the Han river. For developing such system, a procedure was implemented covering user requirement analysis, system design, spatial DB design, and coding. DB linkage with affiliated institutes and cadastral DB updating were proposed as the part of the efforts to enhance the applicability of the system. In addition to that, modularization was adopted for more efficient and cost-effective system development.

• 한국콘텐츠학회:학술대회논문집
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• 한국콘텐츠학회 2006년도 추계 종합학술대회 논문집
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• pp.413-416
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• 2006

본 연구에서는 효과적인 토양보존 및 관리에 필요한 전략적 접근 방법을 제시하였다. 이를 위해 탁수발생이 뚜렷이 구분되는 안동호와 임하호 유역을 선정하였으며, 탁수발생 원인인 토사유실을 평가하기 위해 RUSLE 토사유실모델을 이용하였다. 토사유실 가능성이 높은 지역들은 GIS에 의한 지형특성을 기초로 분석되어질 수 있으며, 특히 상하류 유역이나 인간의 활동영역인 하천주변 특성들을 이용하여 검토할 수 있다. 본 연구에서 제안된 모델링 결과는 토양보존 및 관리를 위해 검토되어지는 토사유실 원인지역을 선정하기 위한 가이드라인으로 활용될 수 있다. 또한 이러한 접근방법은 상대적으로 간편하며, 실질적으로 널리 활용될 수 있다.

• 한국물환경학회지
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• 제32권5호
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• pp.465-474
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• 2016

Since Gyungan stream is included in the protected zone of the water supply source of the Metropolitan area in Korea, the water quality needs to be continuously managed. Therefore, a measure is required that can inhibit the flow of water pollutant into the water body and facilitate the ecological restoration of riparian vegetation. A field survey was conducted on the hydrological characteristics of the landscape elements established on the downstream catchment of the Gyungan stream, the result of which showed that the paddy field and urbanized area can be regarded as point pollution sources. The upland field can be regarded as a non-point pollution source. In order to improve the water quality in the Paldang lake, we first recommended creating a riparian vegetation belt. We also suggested introducing a treatment wetland and an artificial plant island to places in which the creation of a riparian vegetation belt is not ensured. We recommend creating a treatment wetland equipped with diverse functional groups. For creating the plant island, we recommend Zizania latifolia and Typha orientalis, which showed the highest productivity among aquatic plants. The former could be introduced around the outlet of a paddy field and the estuary of tributaries, while the latter could be introduced to a water body directly sourced from mountainous land.