• 해양환경안전학회지
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• 제28권spc호
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• pp.44-49
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• 2022

해양환경의 위험유해물질 배출규제는 주로 선박이나 해양시설 등으로부터의 오염규제에 한정되어 있기 때문에, 해안 인접 산업시설들의 위험유해물질 배출 허용기준 및 배출 지침 수립 등의 해양배출제도의 수립 필요성이 제기되고 있다. 본 연구에서는 해양산업시설의 위험유해물질 배출 허용기준 및 배출 지침 정보를 자세히 제공하고 있는 미국 환경보호청(US EPA)의 자료를 중심으로 허용기준 및 배출 지침 수립 등 배출 제도 체계를 소개하고 향후 국내 배출지침 적용에 대해 고찰했다.

• 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.

• 한국환경교육학회지:환경교육
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• 제15권2호
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• pp.1-13
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• 2002

The progress of environmental science and technology in the developed countries has been rapid in recent years. Particularly remarkable has been the advancement of various pollutant control measures, which have brought the pollution of inorganic factors such as air and water under control. In contrast, diversity of the ecosphere, of which man is a part, is being steadily impoverished and the biological community is getting unvaryingly uniform. These phenomena were brought about by the expansion of artificial environment such as new industrial complexes, transportation facilities and urban development. Man has constructed uniform and artificial environment, believing in the premise of confrontation with nature, to such a scale that the natural environment and biological community have lost their balance. This will increasingly endanger the soundness of the biotic environment of nature, which constitutes the potential foundation both for the survival environment of man as biological entity and for the development of human civilization. In order to guarantee the soundness of man's body, intelligence and sensitivity as wholesome gene pool on the earth and for the future of man, primarily important environmental education is the understanding of how man can everlasting exist in and with the survival environment. In view of this reality, it is vitally important to create ecologically diverse and well-balanced environment with living materials, i.e., vegetation in order to secure lasting survival environment for man. This task is urgently required in highly artificial environment where non-biological materials have forced the impoverishment of the biological community. Therefore, environmental education for the future should not be totally oriented to technology as that in the past nor it is limited to the medical aspect where well-being of human is the sole object of concern. That is to say, environmental education for the future should be one that provides knowledge that human can understand his place based on the ecological concept and thereby make him to have ethical consciousness that he can control his behavior within the reasonable level for ecological niche who he is located.

• 한국환경교육학회지:환경교육
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• 제15권1호
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• pp.137-147
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• 2002

The progress of environmental science and technology in the developed countries has been rapid in recent years. Particularly remarkable has been the advancement of various pollutant control measures, which have brought the pollution of inorganic factors such as air and water under control. In contrast, diversity of the ecosphere, of which man is a part, is being steadily Impoverished and the biological community is getting unvaryingly uniform. These phenomena were brought about by the expansion of artificial environment such as new industrial complexes, transportation facilities and urban development. Man has constructed uniform and artificial environment, believing in the premise of confrontation with nature, to such a scale that the natural environment and biological community have lost their balance. This will increasingly endanger the soundness of the biotic environment of nature, which constitutes the potential foundation both for the survival environment of man as biological entity and for the development of human civilization. In order to guarantee the soundness of man's body, intelligence and sensitivity as wholesome gene Pool on the earth and for the future of man, primarily important environmental education is the understanding of how man can everlasting exist in and with the survival environment. In view of this reality, it is vitally important to create ecologically diverse and well-balanced environment with living materials, i.e., vegetation in order to secure lasting survival environment for man. This task is urgently required in highly artificial environment where non-biological materials have forced the impoverishment of the biological community. Therefore, environmental education for the future should not be totally oriented to technology as that in the past nor it is limited to the medical aspect where well-being of human is the sole object of concern. That is to say, environmental education for the future should be one that provides knowledge that human can understand his place based on the ecological concept and thereby make him to have ethical consciousness that he can control his behavior within the reasonable level for ecological niche who he is located.

• 한국습지학회지
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• 제9권2호
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• pp.1-8
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• 2007

최근 환경정책의 변화는 수질오염총량관리제 및 비점오염원관리로 요약된다. 이는 과거 30년 동안의 급격한 환경기술의 발전에도 불구하고 상수원수인 수질의 악화에 기인한다. 수질오염총량관리제란 환경시설에서의 농도규제가 아닌, 하천에서의 비점오염원을 포함한 총량규제를 위한 제도로 점오염원관리와 더불어 비점오염원 관리가 필수적으로 요구된다. 비점오염원이란 각종 토지이용을 의미하며, 개발사은 비점오염원의 부하량 증대에 큰 영향을 끼치는 원인이다. 이에 개발사업에 따른 비점오염원을 제어하기 위해서 비점저감시설등의 설치가 의무화 되고 있다. 비점저감시설 중 자연형 비점관리시설등의 규모산정에 관한 내용은 환경부에서 제시하고 있으며, 이에 관한 규정에서 강우량 해석을 기초로 하여 시설의 규모를 산정할 것을 요구하고 있다. 본 연구에서는 리조트 스키장 개발사업에서 발생 가능한 비점오염물질을 처리하기 위한 자연형 비점오염물질관리시설인 저류지의 규모를 산정하기 위하여 최근 5년간 및 10년간의 강우사상을 분석하였다. 강우량 해석을 통하여 적정 처리를 위한 강우량을 해석한 결과, 적정 저류지 용량은 누적강우량 기준으로 7.4mm가 가장 경제적인 것으로 나타났다.

• 환경정책연구
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• 제8권1호
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• pp.97-127
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• 2009

독일에 있어서 북해와 동해는 여러 측면에서 매우 중요한 의미를 가지고 있다. 북해의 연안국에게 북해변의 경제적 의미가 매우 크다. 이곳에는 수많은 항만들 외에 많은 공업시설이 있으며, 이곳은 또한 농업 발달지역이기도 하다. 바닷물과 강물이 섞인 곳(Brackwassermeer)인 동해의 특징은 북해와는 협수로 연결이 되어서 북해와의 물의 순환이 원활하지 못한 지정학적 위치 때문에 북해처럼 빠른 속도로 유해물질이 처리될 수 없다는 점이다. 크고 작은 선박사고 및 각종 오염 원으로부터 보호하기 위해 동해는 특히 HELKOM협약을 통하여, 그리고 북해는 OSPAR협약을 통하여 노력을 기울이고 있다. 또한 선박사고 시 예인선에 관하여 NethGer-Plan과 DenGer-Plan을 통하여 네덜란드와 독일, 덴마크와 독일간에 협조가 이루어지고 있다. 1995년에 브레멘 부근에서 발생한 팔라스(Pallas)호 사건 이후 독일에서는 미래의 해양안전을 위해서 사용가능한 자원에 대한 연안 각 주간의 협조가 개선되어야 할 필요성이 증대되었다. 그 결과 2003년 1월 1일에 연방과 연안 주정부들은 공동으로 하바리 코만도(Havarie-Kommanando 선박사고 대책부대)를 조직하였다. 하바리 코만도는 중대한 선박 사고 발생 시 대국민작업 및 선박 사고 관련 조직의 동원을 통합적으로 지휘하는 업무를 담당하는 것을 골자로 각 업무별 담당기관의 조정을 위한 연방-주 공동 기관이다. 또한 해상에서의 비상사태 시 연방과 주의 참여기관, 각 해운회사, 헬리콥터 회사인 Hiking-Helicopters-Service 등과의 협동이 잘 이루어지고 있으며, 동해 최대 여객선사인 독일-덴마크 선박회사인 Scandlines, ARGE Kuestenschutz와도 공조가 잘 되고 있다.

• 대한지하수환경학회지
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• 제4권4호
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• pp.175-184
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• 1997

부산 석대 생활폐기물 매립지는 1987년 6월부터 1993년 5월까지 만 6년간 사용된 중간규모의 매립장이다. 매립장에 분포하는 안산암질암과 유문암질암에는 절리와 단층이 발달되어 있다. 1996년 7월과 1997년 6월에 2차에 걸쳐 침출수, 하천수 및 지하수의 수질을 조사한 결과 침출수와 하천수의 수질은 농도가 약간 감소되었으나, 지하수 수질은 더 악화되었다. 석대매립지의 지하수 오염은 충적층에 개발된 천층지하수는 물론이고, 150m 심도의 암반지하수들도 오염이 심화되어 있다. 침출수에 의한 지하수 오염범위는 매립장 경계에서 서쪽으로 약 500 m 정도, 남쪽으로 약 1 km 정도 까지이다. 석대 매립지 주변 수질의 오염제어를 위해서는 매립지 일윈에 감시정 및 채수정의 개발, 침출수처리장 건설, 기존의 지하 차수벽시설 보완작업 등이 필요하다.

• 한국환경과학회지
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• 제19권6호
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• pp.665-670
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• 2010

Pollutants from urban pavement consists various kinds of substances which are originated from dry deposition, a grind out tire, corrosive action of rain to pavement and facilities and raw materials of the road etc.. These are major pollutants of urban NPS (Non-point source) during rainfall period. However there is not enough information to control such pollutants for appropriate management of natural water quality. In this study of transportation areas, three monitoring stations were set up at trunk road, urban highway and national road in Gyeongnam province. Runoff flow rate was measured at every 15minutes by automatic flow meters installed at the end of storm sewer pipe within the road catchment area for water quality analysis. Data was collected every 15 minutes for initial two hours of rainfall. Additional samples were collected 1-4 hours interval till the end of rainfall. The monitoring parameters were $COD_{Mn}$, SS, T-N & T-P and heavy metals. The average EMCs of TSS and $COD_{Mn}$ were 62.0 mg/L and 24.2 mg/L on the city trunk road, which were higher than those of urban highway and national road, indicating higher pollutant loads due to activities in the city downtown area beside the vehicle. On the other hand, the average EMC of T-N and T-P were in the range of 2.67-3.23 mg/L and 0.19-3.21 mg/L for all the sampling sites. Heavy metals from the roads were mainly Fe, Zn, Cu and Mn, showing variable EMCs by the type of road. From the TSS wash-off analysis in terms of FF(first flush) index, first flush phenomenon was clearly observed in the trunk road(FF : 0.89-1.43). However, such mass delivery behavior was not apparently shown in urban highway(FF : 0.90-1.11) and national road(FF : 0.81-1.41).

• 한국습지학회지
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• 제11권2호
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• pp.55-66
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• 2009

비점오염원에 의한 4대강의 오염부하증가율이 점점 증가하고 있어 비점오염원 관리의 필요성이 증대되고 있다. 따라서 환경부는 수질오염총량관리제를 도입하여 수생태계 입장에서 수질개선 정책을 펼치고 있으며, 한강 수계를 비롯한 4대강 유역에 비점저감시설을 설치하여 시범사업을 실시하고 있다. 그러나 현재 적용되어 운영되고 있는 비점오염저감시설은 대부분 외국의 기술을 그대로 이용한 것으로 처리성능 및 효율의 불확실성과 기후 및 유역특성을 반영하고 있지 않는 등 많은 문제점을 안고 있다. 따라서 본 연구는 고속도로내 톨게이트와 주차 장지점에 비점오염저감시설을 설치하여 2~3년 동안 운전하였으며, 비점오염물질의 유출특성과 저감시설의 오염 물질별 제거형태를 파악하였다. 이러한 결과는 비점오염물질 관리를 위한 토지이용별 비점저감시설의 적용, 운영 및 유지관리에 활용될 수 있을 것으로 기대된다.

• 제어로봇시스템학회:학술대회논문집
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• 제어로봇시스템학회 2005년도 ICCAS
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• pp.2036-2041
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• 2005

The underwater multi-agent technology has many potential for the various activities related to ocean development/conservation in the near future. For example, in such fields as water pollution investigation, aquaculture control, or coral reef research, we feel a growing need for a system that realizes underwater continuous monitoring in the wide rang e. In this case, the target monitoring area will be sliced planar hierarchically toward the depth as monitoring layers, and many AUVs arranged on each layer track the given trajectory and gather various environmental information continuously, with communicating each other in the layer or with other layers. To realize those systems we need to develop AUV multi-agent technologies. So we are now building basic systems for basin experiment for the development of AUV multi-agent behavior. We must experience many situations and problems to be solved for the development of its elemental technologies by using real systems as well as our computer simulations. In this paper we introduce our concept of the experiment in the near future and the hardware/software design of our two types of handy AUVs and ultrasound ranging/communication system for that experiment. One AUV is designed using a 17inches-diameter glass sphere with DOS/V and RT-Linux based subsystems, which is intended to use not only in the basin but also in the calm real sea. The other AUV is designed for the basin experiment using a 7inches-diameter acrylic sphere with low-cost embedded system with SH-2 based subsystems. The basin experiment to verify the basic AUV facilities and ultrasound ranging for position detection was carried out.