• Title/Summary/Keyword: 기름오염사고

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흡착재를 사용한 기름회수기 개발의 기초연구

  • 권병곤;고경찬;박외철
    • Proceedings of the Korean Institute of Industrial Safety Conference
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    • 1997.11a
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    • pp.235-242
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    • 1997
  • 환경문제에 관한 관심이 급속히 증가하고 있는 가운데, 1995년 여름 유조선 씨 프린스호의 여천 앞바다 좌초로 다량의 기름이 유출되었다. 이 사고 이후 두달이 채 지나기도 전에 유조선 제1유일호가 부산 앞바다에서 침몰하는 사고가 발생했다. 통계1)에 의하면, 1991년 1월부터 1995년 9월말까지 우리나라 연안에서 총 1,583 건의 오염사고가 발생하였고, 유출량은 22,541톤, 피해금액 3,231억원으로 집계되었다. 해양오염사고중 기름에 의한 오염사호는 총발생건수의 92%로 대부분을 차지하고 있다. 배출원인은 선박사고가 전체 발생건수의 87%, 육상 및 해양시설에 의한 사고가 10.5%, 배출원인 불명이 2.5%였다. 오염물질 중 기름의 종류별 유출랑은 경유 6,509톤, 벙커유 3,928톤, 선저폐수 759톤으로, 경유가 가장 많고 다음으로 벙커유가 많았다. 해상 기름유출사호는 기름운반선 등에 의해 하루에 한번 꼴로 크고 작은 기름유출사고를 일으키고 있으며, 발생건수가 매년 증가하고 있다. 우리나라 연안에서의 유류 해상 수송량 증가와 선박의 대형화로 대형기름유출사고의 발생 가능성이 잠재하고 있다. (중략)

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Overview of Major Oil Spill at Sea and Details of Various Response Actions 2. Analysis of Marine Oil Pollution Incidents in Korea (대형 기름유출사고와 방제조치에 관한 연구 2. 국내 해양 기름오염사고 분석)

  • Kim, Kwang-Soo
    • Journal of the Korean Society of Marine Environment & Safety
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    • v.19 no.5
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    • pp.467-475
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    • 2013
  • In order to seize quantitative materials as part of studies on measures for oil pollution prevention and control, the statistics of oil pollution incidents in Korean coastal waters for 10 years from 2003 to 2012 were analyzed with relation to the number of oil spills and the volume of oil spilt according to causes, sources and sea areas of spills. Total number and total volume of oil spills for 10 years were found to be 2,833 cases and 17,877 kL, respectively. 50.4 %(1,429 cases) of total number of oil spills were caused by negligence, although oil spillage due to negligence was 294 kL(1.7 %). While oil spillage caused by marine accidents was 17,400 kL(97.3 %), marine accidents accounted for 27.9 %(790 cases) of total number of oil spills. While negligence had a great influence on the number of oil spills, marine accidents had a huge impact on the amount of oil spilt. Fishing boats accounted for 42.7 %(1,210 cases) of the number of oil spills, and although oil tankers accounted for 9.2 %(261 cases) of the number of oil spills, oil spillage from oil tankers was 15,488kL(86.7 %). It means that oil tankers such as VLCC or ULCC may be the main sources of major oil spills and a few very large spills are responsible for a high percentage of the amount of oil spilt. While the number of oil spill incidents was closely related to the accidents of fishing boats, the volume of oil spilt was greatly affected by the major oil spill incidents of oil tankers such as M/T Hebei Spirit. The number and volume of oil spills were shown to be 1,613 cases(56.9 %) and 3,804 kL(21.3 %) in South Sea, 700 cases(24.7 %) and 13,501 kL(75.5 %) in West Sea, and 520 cases(18.2 %) and 572 kL(3.2 %) in East Sea of Korea, respectively. The highest number of oil spills was found in South Sea and the most volume of oil spilt was shown in West Sea of Korea for 10 years.

Overview of Major Oil Spill at Sea and Details of Various Response Actions -1. Number and Volume of Marine Oil Spills in Korea and in the World (대형 기름유출사고와 방제조치에 관한 연구 -1. 국내외 해양기름오염사고 건수와 유출량)

  • Kim, Kwang-Soo
    • Journal of the Korean Society of Marine Environment & Safety
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    • v.19 no.2
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    • pp.129-137
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    • 2013
  • In order to obtain quantitative basic data for marine oil pollution prevention, the statistics of oil spill incidents in Korea and in the world for 20 years from 1993 to 2012 were collected and analyzed with relation to the number of oil spills and the amount of oil spilt. In Korea for 20 years, total number and average annual number of oil spills were 6,608 cases and nearly 330 cases/year, respectively, and total volume and average annual volume of oils spilt were 57,328 kL and nearly 2,866 kL/year, respectively. Due to major oil spills from oil tankers, annual volumes of oils spilt in Korea were sharply increased to 15,388 kL in 1993, 15,773 kL in 1995, 3,428 kL in 1997 and 13,008 kL in 2007. In case of worldwide oil spills for 20 years, total number and average annual number of oil spills of 8 kL (or 7 tonnes) and above were 420 cases and 21 cases/year, respectively, and total amount and average annual amount of oils spilt 8 kL (or 7 tonnes) and above were about 800,000 kL (or 704,000 tonnes) and about 40,000 kL/year (or 35,200 tonnes/year), respectively. Major oil spills from oil tankers increased massively annual amounts of oils spilt worldwide to about 159,000 kL (or 140,000 tonnes) in 1993, about 147,600 kL (or 130,000 tonnes) in 1994, about 90,900 kL (80,000 tonnes) in 1996, about 81,800 kL (72,000 tonnes) in 1997 and about 76,100 kL (or 67,000 tonnes) in 2002. Obvious correlation between annual number of oil spills and annual amount of oil spilt was not found in both Korea and the world, while both annual number and annual volume tended to decrease with the lapse of year in both Korea and the world, though there were wide fluctuations from year to year in both annual number of oil spills and annual amount of oils spilt worldwide and in Korea for 20 years. From 2008 to 2012 worldwide, there were sharp decreases in both annual number and annual amount of oil spills. In particular, no oil spill of 800 kL (or 700 tonnes) and above occurred in the year of 2012.

The Effectiveness of the Dispersant Use during the "Deepwater Horizon" Incident -REVIEW of the Proceedings from 2011 International Oil Spill Conference- (미국 멕시코만 기름유출사고에서 본 유처리제 사용의 효용성 고찰)

  • Cho, Hyun-Jin;Ha, Chang-Woo
    • Journal of the Korean Society of Marine Environment & Safety
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    • v.18 no.1
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    • pp.61-65
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    • 2012
  • Once oil has spilled, oil spill responders use a variety of countermeasures to reduce the adverse effects of spilled oil on the environment. Mechanical methods of containment and recovery are preferred as the first response when the use of other methods fail or are ineffective. In these cases, the application of oil dispersants shall be use only as a last resort. While effectiveness of dispersants in removing oil form the sea surface is proven, the use of dispersants is controlled in almost all countries due to the toxicity of their active agents and the dispersed oil on the marine environment. However, according to reports, after dispersant application, no significant toxicity to fish or shrimp was observed in the field-collected samples. Moreover, the results also indicate that dispersant-oil mixtures are generally no more toxic to the aquatic test species than oil alone. During the Deepwater Horizon Incident, dispersants were applied to floating oil and injected into the oil plume at depth. These decisions were carefully considered by state and federal agencies, as well as BP, to prevent as much oil as possible from reaching sensitive shoreline habitats. Net Environmental Benefit Analysis for dispersant use assumed that dispersants appear to prevent long-term contamination resulting absence of oil in the substrate and will benefit marine wildlife by decreasing the risk of significant contamination to feathers or fur. Further study to use dispersants with scientific baseline is needed for our maritime environment which consistently threaten huge oil spill incidents occurrence.

방제단계 측정도구 개발에 필요한 주요요인 선정에 관한 연구

  • Mun, Jeong-Hwan;Yun, Jong-Hwi
    • Proceedings of the Korean Institute of Navigation and Port Research Conference
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    • 2012.10a
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    • pp.8-9
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    • 2012
  • 우리나라 해양에서 발생 가능한 기름유출사고를 소형 중형 대형으로 구분하여 대비 대응이 가능한 방제세력이 구축되어 있으며, 이 3단계를 구별하는 기준은 "유출량"이다. 그러나 유출량 외 반드시 고려되어야 할 요인이 누락되어 있는 실정이다. 1967년 이후 발생한 주요한 20건의 해양오염사고에서 대규모의 유출량을 발생한 해양오염사고라도 환경적으로 유출지점이 연안에서 상당한 거리에 떨어져 있을 경우에는 피해가 없거나, 거의 발생하지 않은 사고들도 포함되어 있다. 이처럼 해양에서 발생 오염사고는 오염에 직접적으로 영향을 미치는 기름의 유출량뿐만 아니라 사고가 발생한 해역의 위치 등 여러 가지 요인을 복합적으로 고려하여 방제조치를 실시해야 한다. 따라서 이 연구에서는 방제수행에 있어서 필요한 고려요소를 재정립하고자 한다.

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Application and Assessment on the Effectiveness of the Hazard-Based Deployment Model for Oil Recovery Capacity on Water (위해도 기반 해상기름회수능력 배치모델 적용 및 유효성 평가)

  • Ha, Min-Jae;Moon, Jung-Hwan;Yun, Jong-Hwui
    • Journal of the Korean Society of Marine Environment & Safety
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    • v.20 no.5
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    • pp.486-490
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    • 2014
  • In this study, the Hazard-based model to decide regional oil recovery capacity by using AHP is suggested and regional oil recovery capacity is calculated by applying the model. The simulation for oil recovery capacity by mobilization of regional oil recovery equipments is carried out to verify the availability of the model. The worst oil spill accident in Daesan Taean Pyeongtaek region, which is located in geographically disadvantageous position among the regions that the worst oil spill accident may occur, is supposed for the simulation. As a result of simulation, the quantity of oil that can be recovered for three days on the scene of oil spill accident is worked out as $15,841k{\ell}$, which can satisfy the goal of national oil recovery capacity for the worst oil spill accident, therefore the model is verified as practicable.

해양오염 모니터링 및 방제지원 시스템 설계

  • Yang, Chan-Su
    • Proceedings of the Korean Institute of Navigation and Port Research Conference
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    • 2009.10a
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    • pp.9-10
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    • 2009
  • 해상에서 선박사고에 의한 기름 유출 시, 기름의 위치, 변화과정, 이동 특성을 신속하게 파악하고 예측하는 것은 방제전략에 있어 필수적 요소이다. 따라서 사고 이후의 유출의 현황 정보의 수집은, '유출유 대응 매뉴얼'(IMO, 1988; ITOPF, 2008) 에서 가장 우선시 되고 있다. 일반적으로 유출유 탐지는 선박, 항공기 및 인공위성을 이용한 방법이 사용되고 있으며, 최근 인공위성기술의 발전에 따라, 국제유조선선주오염방지연맹(ITOPF)에서는 인공위성 원격탐사 기술 적용을 통한 유류 모니터링 적용을 권장하고 있다 (ITOPF, 2008). 허베이스피리트호 원유유출 사고는 2007년 12월 7일 아침 7시 6분경 서해안 만리포 북서쪽 10km 해상에서 크레인을 적재한 1만1800t급 바지선이 정박 중인 홍콩 선적 유조선 허베이 스피리트호(14만6000t급)와 부딪치면서 발생했다. 국내에서는 원격탐사를 이용한 기술지원체계가 갖춰져 있지 않기 때문에, 이번 사고의 경우에도 실질적인 지원이 이루어지지 못했다. 본 연구에서는 원격탐사에 의한 유류오염 사고 시 유출유 탐지 및 추출 그리고 정보의 가시화 좌표화를 통해서 실질적인 방제지원시스템을 개발하기 위한 연구 개발의 중간보고를 하기 위한 것이다.

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Remove and analysis of spilled oil and compensation for the damage caused by spilled oil (유출유의 방제, 분석 및 피해보상에 관하여)

  • Kim, Do-Hee
    • Proceedings of KOSOMES biannual meeting
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    • 2008.05a
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    • pp.115-116
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    • 2008
  • A big accident of oil spill occasionally occur in coast of Korea according to increase of sailing of oil tank ship in recently. This study was focused on transformation and behavior of spilled oil in ocean and effect of spilled oil on environment and introduce the methods of analysis of spilled oil, compensation for the damage caused by spilled oil.

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