초록 ▼

〇 원격관측망 분야 (예측 모델링 지원)
- 13Mhz 고주파 레이더를 제주 김녕 및 애월에 설치하여 단기시범운영 실시. 방통위의 허가를 얻어 김녕에는 안테나 고정 설치, 운영 중. 애월에는 2011.12. 6 허가통보를 받아 12월 중순 설치 예정.
- SAR 위성정보 이용 유출유 감시 기반 구축. 태안, 다렌항, 보하이만 사고에 활용
- WCDMA 3G 통신 이용 표면 유출유 소형 추적부이 제작, 선박 레이더를 이용한 유출유 추적 기술 개발 및 모사체 현장실험
〇 예측모델망 분야 (연안순환 및 유

〇 원격관측망 분야 (예측 모델링 지원)
- 13Mhz 고주파 레이더를 제주 김녕 및 애월에 설치하여 단기시범운영 실시. 방통위의 허가를 얻어 김녕에는 안테나 고정 설치, 운영 중. 애월에는 2011.12. 6 허가통보를 받아 12월 중순 설치 예정.
- SAR 위성정보 이용 유출유 감시 기반 구축. 태안, 다렌항, 보하이만 사고에 활용
- WCDMA 3G 통신 이용 표면 유출유 소형 추적부이 제작, 선박 레이더를 이용한 유출유 추적 기술 개발 및 모사체 현장실험
〇 예측모델망 분야 (연안순환 및 유출유 거동 예측)
- 기상연구소 WRF 모델 결과와 한국과학기술정보연구원의 고성능 컴퓨팅 자원 • 환경을 이용하여 ROMS 모델 기반의 황동중국해 모델을 구축, 72시간 예보 기반 구축. 서해, 남해, 동해 모델 구축. 200m 군산 해역 모델을 이용 HF radar 자료동화기법 개발.
- 미국 NOAA와 협력으로 3차원 유출유 거동 예측 모델 개발, GIS 기반 예측 시스템 구축. 중국 다롄항, 보하이만 사고 등에 활용.
〇 오염 진단평가 및 분석 기술 분야
- 오염 신속진단 기법 개발, WAF 및 CEWAF 제작 표준화 후 요각류 및 부착미소생물군집에의 영향 분석, 메조코즘을 이용한 유분산제의 부유생태계 영향 분석.
- 가격대비 성능측면에서 양호한 암반부착 기름 제거용 Biosolvent 탐색
〇 선박파손부 긴급 봉쇄장치 개발
- 영구자석 기반 고압 소형 및 저압 장대형 장치 개발. 해양경찰청 방제훈련 프로그램에 활용.

(출처 : 보고서 요약서 3p)

Abstract ▼

IV. Research outcome
(1) Establishment of remote observation system
O Installation of HF radar and short-term measurements
- Short-term measurements of sea surface current in the Jeju Strait were carried out using HF radar temporarily installed at Aewol and Gimnyeong. It was found that th

IV. Research outcome
(1) Establishment of remote observation system
O Installation of HF radar and short-term measurements
- Short-term measurements of sea surface current in the Jeju Strait were carried out using HF radar temporarily installed at Aewol and Gimnyeong. It was found that the overall observed area did not exceed the expected observation area. There was however some environmental interference affecting on sea surface current measurements which in turn results in some change in observation area. Erroneous data and missing values were interpolated.
- Antenna unit at Gimnyeong is in operation. Delay in getting permission from KCC (Korea Communications Commission) however resulted in delay in deployment of HF radar at Aewol, inhibiting the production of data. It is expected that KCC permission is granted soon and time series data from HF radar of Aewol will be then available
O Development of sea surface spilled oil tracking buoy
- SBAS(Satellite Based Augmentation Systems) was selected as GPS for the tracking buoy positioning. Experiments showed that the mean positioning error was less than lm with standard deviation less than 1m to the East-West direction, 1.5m North-South direction, indicating that the system is sufficiently accurate to use in oil spill tracking.
- Type C of a disc shape with 32mm in height was finally chosen because the consistency of the experimental results and the correlation with current with were very good. The buoy positions are telecommunicated using WCDMA 3G. Hardware and software were developed to monitor the buoy movement in mobile condition as well as at a remotely located room.
O Development of oil spill tracking technology using ship-mounted radar
- Comparison of a range of filtering methods associated with oil spill detection shows that gamma filtering is most appropriate to discrimination of spilled oil area. Application of wavelet analysis to the filtered image is found to be helpful in deducing the boundary of spilled oil.

(2) The prediction modeling system
O Meteorological information system
- The model WRF09 was applied to produce meteorological information for the hindcasting of Sea Prince oil spill in 23 July, 1995, covering the passage of typhoon Faye. Bogussing effects were examined comparing the 48hr forecast central pressure and maximum wind speed at 12 UTC July 22, 1995. Comparison of results shows that the model with typhoon bogussing scheme produces the best track of RSMC-Tokyo with decrease of the central pressure almost 20~30 hPa and with improvement in calculating maximum wind speeds, while the model WRF09 without a typhoon bogussing scheme clearly underestimates the typhoon strength and wind speed.
- Higher resolution marine meteorological information system (WRF03) was alos developed. The lateral boundary condition of the system come from WRF09 (9km resolution). Marine information such as mean sea level pressure, surface temperature, relative humidity, radiation and wind speed were delivered to NAP co-workers for the use as forcing data of the ocean circulation model.
- Calculation of wave climate around Korean Penisula was also carried out. Monthly and 10-day averaged data for significant wave height and direction were produced by the high resolution regional wave forecasting system (ReWW3 ： Regional WAVE WATCH III) at KMA during March 2008 to February 2011 and send the data to KORDI for ocean pollution prediction system.
O Development of circulation models
- Development of multiply-nested circulation modeling system covering the marginal seas around the Korean Peninsula to provide near-real time realistic currents which is essential for the response to marine pollution accidents.
- Development of local coastal models with fine resolution
- Development of assimilating technique of HF radar information to improve the prediction accuracy
O Development of oil spill models
- The developed 3D model was applied to Hebei Spirit oil spill incident occurred on Dec 7, 2007, comparing results with those from NOAA’s GNOME and with satellite images (ENVISAT image on 10:40 Dec 11, 2007, and Radsat image on 18:31 Dec 11, 2007). It was confirmed that correct specification of oil releasing information is important.
- The model was also applied to oil spills in Bohai Bay of China occurred on June 3, 2011. The oil releasing scenario was analyzed through the comparison with SAR satellite image.
- For the establishment of user friendly operating system GIS-based GUI system was developed. The system has functions of reading and displaying the electric navigation charts as well as defining input and output options. From the model-generated results informations such horizontally 2D distribution, 3D distribution, and vertical behaviour of the spilled oil, and time variation of weathering process are displayed using GIS-based graphic form.
- Supplementary investigation on oil spill modeling was made appying MOHID and IMMSP oil spill models to Hebei Spirit oil spill incident. It was found that the accuracy of the circulation model and the resolution of the oil spill model are critical to the determination of prediction accuracy of oil spill behaviours.
O Establishment of Grid portal environment
- The high-performance computing resources was provided for the development of oil spills prediction model with support of prediction model users which include in detail, the Supercomputer IV and the high-performance Linux clusters.
- Using Grid portal, real-time simulation environment for prediction model and real-time integrated system for marine pollutants prediction were provided. In detail, the Web portal of ROMS model for seawater flow was developed using the TIGRIS infrastructure and WSRF-based Grid services (KMI-R2). The integrated system was designed through the analysis of current marine pollution forecasting system, service scenarios and user requirements.

(3) Development of contamination analysis · assessment and cleaning technologies
O Contamination analysis · assessment technologies
- On-site fluorometric detection method for oil contamination： A fluorometric on-site analysis method for the evaluation of oil contamination was developed, validated and compared with a conventional gas chromatographic (GC) technique. The method was applied to an actual oil spill case and applicability of the method was confirmed. The introduced fluorescence method was capable of generating data comparable to that of GC, but more rapidly and cost-effectively, so that it can be favorably used as a quick screening method for rapid decision making and responses.
- On-site detection methods for fish oil exposure: The value of this approach is that is a simple and rapid method of assessing the extent of exposure of fish to PAH using 96-well plate reader by fixed wavelength fluorescence. It can use a reliable indicator of current or recent PAH exposure in resident fish on oil spill sites.
- Optimization of WAF & CEWAF preparation method： Most of toxicity tests for spilled oil are conducted using water accommodated fraction (WAF) or chemically enhanced water accommodated fraction (CEWAF) of oil, which simulate physically and chemically dispersed oil in water, respectively. As each laboratory uses different preparation method for WAF and CEWAF, it is very difficult to directly compare the results produced by different laboratories. This study aimed to optimize the preparation methods for WAF and CEWAF to check effects of various parameters like mixing speed, mixing time, settling time, vessel size and storage time according to Singer et al. (2000).
- For WAF, mixing speeds (110 and 200 rpm) do not significantly (p > 0.05) affect total petroleum hydrocarbon (TPH) level in WAF. TPH concentrations reached saturation after 24 hrs mixing. Vessel size affected the TPH in WAF mainly due to the specific surface area of each vessel. TPH concentration of WAF stored in refrigerator demonstrated slight reduction for the first 12 h and remained constant for 8 days. For the preparation of CEWAF, oil to dispersant ratio, 1:10 was used under mixing energy of 20~25% vortex of solution height.
To see the effects of resurfacing of large droplet, TPH concentrations in filtered and non-filtered solutions were compared. 18 hrs of mixing time and 6 hrs of settling time was found to be most optimized condition for chemically dispersed oil.
Toxicities of WAF, GEWAF on the copepod Tigriopus japonicus: We determined the toxicity of water accommodated hydrocarbon fractions (WAF), two chemically enhanced WAFs (CEWAFs； CEWAF-C, Crude oil + Corexit 9500 and CEWAF-H, Crude oil + Domestic product A) of crude oil and two dispersants (Corexit 9500 and Domestic product A) for the rock pool copepod Tigriopus japonicus. In the acute toxicity test, Corexit 9500 was the most toxic amongst all the chemicals. In result, as nauplius stage of T. japonicus was more susceptible than their adult female when exposed to toxic chemicals, the toxicity data using nauplius would be considered in order to decide spiking concentration of chemical for chronic toxicity test on the copepod. In the two generations (F0 and F1) chronic toxicity test, survival, sex ratio, developmental time and fecundity of the copepod exposed to several toxic chemicals showed various responses to different concentrations of chemicals. The chemicals used in this study except for Product A caused accumulation of toxicity. The lowest concentrations of WAF, CEWAF-H, CEWAF-C, and Corexit 9500 affected through two generations were 50%, 50%, > 5% and 1%, respectively.
Mesocosm study for the environmental fate of spilled oil: Once in the marine environment, the spilled oil is immediately subject to a variety of weathering processes, including evaporation, dissolution, emulsification, microbial degradation, photo-oxidation, adsorption to suspended matter, and deposition on the sea floor, that determine its ultimate fate and impact on the environment. In this study, long-term fate of physically and chemically dispersed oil in the water column were monitored using mesocosm. Nine sets of experimental bag with capacity of 1,000 L had been exposed to non-oil control (x3), oil only (x3), and pre-mixed oil+dispersant (x3) for 77 days. A much faster increase of oil concentration (TPH) in the water column was observed in the oil+dispersant bag (313 ㎍/L/day) than in the oil only one (3.5 ㎍/L/day) till eight days after oil addition. Oil concentrations in the water column remained relatively constant thereafter. TPH levels in the oil+dispersant bag were about two orders of magnitude higher than those in the oil only bag. At the initial stage of the spill TPH levels showed distinct differences according to the depth, that is, surface (0.5 m) > middle (2.5 m) > bottom (4.5 m). But these vertical differences disappeared 33 and 77 days after the spill in the oil only bag and oil+dispersant bag, respectively. Distribution pattern of alkane and PAHs indicates that oil only bag is mainly influenced by dissolution, but oil+dispersant bag by dispersion. Temporal variation of PAHs composition showed the preferential degradation of low alkylated PAHs. After the removal of surface oil, hydrocarbons in the water column degraded exponentially. Oil+dispersant bag showed much faster degradation rate (t1/2=8.6days) than oil only bag (t1/2=158days).
A study on the marine planktonic ecosystems using mesocosm: To assess the effects of crude oil and dispersant on marine planktonic ecosystems, analyses were performed in 1, 000-L marine mesocosm over a period of nine days. Triplicate experiments were conducted for two different treatments, namely, addition of crude oil alone and oil plus dispersant. In the mesocosm with oil plus dispersant, high concentrations of TPH were soon found in the bottom layer. In addition, most planktonic communities responded drastically to the presence of dispersant acting to disperse TPH: heterotrophic bacterial abundances increased for the first two days and then decreased rapidly for the remainder of the experiment. The abundance of heterotrophic flagellates increased rapidly in association with the increase in bacterial cells. The abundance of phytoplankton and zooplankton communities decreased clearly within two days. However, most planktonic communities were affected less adversely in the mesocosms treated with crude oil alone than in those treated with both crude oil and dispersant. The present results demonstrate that the planktonic ecosystem was damaged more severely by the introduction of dispersant than by the harmful effects of crude oil itself. Time-delayed relationship revealed that the TPH concentration had a significant negative relationship with phyto- and zooplankton communities within two days. Therefore, caution should be taken when considering the direct application of dispersant in natural environments, even though it has the advantage of rapidly removing crude oil.
Influence of WAF on microecosystem： We induced climax microecosystem using the adhesion characteristics of microorganisms that form various communities in benthic ecosystem. The plate with the climax microecosystem was used to investigate the changes of ecosystem by oil pollution. A dominant adhesive microalgae on the plate was Cylindrotheca closterim and then changed to Navicula directa var, remota follwed by Thalassionema frauenldii. To observe the effect of WAF for adhesive microorganism using microcosm, abundance of adhesive microalgae was decreased by exposure to WAF from 2.14 x 103 cells/cm² to 0.59 x 103 cells/cm². A dominant adhesive microalgae was Th. frauenldii (over 90%). Bacteria and HNF increased after exposure to WAF. Nano-sized adhesive microalgae increased unlike ciliate. Tigriopus japonicas fed WAF-polluted adhesive microalgae showed low ingestion rate. Therefore, WAF caused change of microorganism community and reduction of feeding habit in the copepod.
- Effect of CEWAF on marine microecosystem： In order to study the effect of CEWAF on the attached micro-fauna, we pre-tested at various concentrations of CEWAF (10, 20, 50 and 100%). Adhesive algae grew at concentrations of 0%, 10% and 20% of CEWAF, however, dominant species at 0% CEWAF (Genus Cylindrotheca) was different from 10% and 20% of CEWAF treatment (Genus Entomoneis). Bacteria adapted to all CEWAF treatment but HNF (heterotrophic nano -flagellates) showed different growth at each CEWAF treatment. As the result of the pre-test, 20% CEWAF was applicable concentration for microcosm test. As the result of 20% CEWAF microcosm test, growth of adhesive algae was prevented, but it grew when CEWAF concentration decreased. Bacteria and HNF showed inconstant growth by CEWAF on microcosm test
O Development of oil-removing technologies
- Formula of tentative biosolvent that could remove 60~80% < adsorbed weathered oil from simulated bed-rocks was developed. The price of formulus was 6,000 Korean won per liter and cheaper than commercial low toxic thinner.
- A pilot biosolvent injection equipment was manufactured with temperature and pressure controller and displaying monitor. Test of the equipment performance showed that the pre-processing and composition of biosolvent is most critical to oil removing adhered to rocks. That is, effects of biosolvent injection with high temperature and high pressure was found to be marginal.

(4) Development of technologies of emergently blocking the cracks or holes on the ship hull
O Development of equipments of emergently blocking the small holes with high spilling pressure on the ship hull
- Electric controller type: To stop the oil spilling after the locating the equipment on the target position, electric remote controlling system is used for the attachment and on/off valve operation. The electric power is supplied using waterproof electric motor.
- Air pressure controller type： The same as above except that the controlling power is supplied by the injection of air pressure.
O Development of equipments of emergently blocking the holes or cracks with small spilling pressure on the ship hull
- Blocking equipment for the damaged parts at the comer: The equipment has no on/off valve but can be folded.
- Development of a pilot equipment for the blocking of elongated type of damaged parts
O Development of a equipment for the removal of oil remnant within a ship
- Development of a pilot equipment equipped with drill and motor to remove the small amount of oil remaining within the ship sunken in the shallow water.

(출처 : SUMMARY 23p)

목차 Contents

• 표지 ... 1
• 제출문 ... 2
• 보고서 요약서 ... 3
• 요약문 ... 5
• SUMMARY ... 19
• 목차 ... 35
• 표목차 ... 41
• 그림목차 ... 43
• 제1장 연구과제의 개요 ... 79
• 제1절 연구의 목적 ... 81
• 1. 최종목표 ... 81
• 가. 총괄적 목표 ... 81
• 나. 세부연구목표 ... 81
• 2. 1단계 목표(2008.12~2011.12) ... 81
• 가. 총괄적 목표 ... 81
• 나. 세부연구목표 ... 81
• 제2절 연구의 필요성 ... 82
• 1. 국내적 필요성 ... 82
• 가. 국가적 측면 ... 82
• 나. 경제·사회적 측면 ... 84
• 다. 기술적 측면 ... 84
• 2. 범세계적 필요성 ... 85
• 제3절 연구주제 및 연구체계 ... 86
• 1. 연구주제 ... 86
• 가. 연구주제 도출 과정 ... 86
• 나. 연구주제의 구분 ... 87
• 2. 연구추진체계 ... 88
• 가. 국내 연구팀의 구성 및 역할 ... 88
• 나. 국제협력 기관 ... 89
• 제4절 연구의 범위 ... 89
• 1. 원격관측망 ... 89
• 가. HF Radar를 이용한 표층류 모니터링 시스템 기반 구축 ... 89
• 나. 표면 유출유 추적부이 ... 90
• 다. SAR 이용 유출유 원격탐지 기반 요소기술 개발 ... 90
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 90
• 2. 예측 모델망 ... 90
• 가. 해양기상 정보 모델 개발 ... 90
• 나. 첨단 연안 순환 예측 모델 개발 ... 91
• 다. 첨단 유출유 거동 예측 모델 개발 ... 91
• 3. 오염진단·평가 및 정화기술 분야 ... 91
• 가. 오염 진단 평가 기술 ... 91
• 나. 암반 정화 기술 개발 ... 92
• 4. 선박파손부 긴급봉쇄장치 개발 분야 ... 92
• 가. 선박 파공봉쇄장치 ... 92
• 나. 잔존유 제거장치 개발 ... 93
• 다. 장치 이동설비 개발 ... 93
• 라. 정전기 발생 실험장치 개발 ... 93
• 마. 고·중·저압용 실험장치의 개발 ... 93
• 제2장 국내외 기술개발 현황 ... 95
• 제1절 국내외 관련 분야에 대한 기술개발현황 ... 97
• 1. 원격관측망 ... 97
• 가. HF radar를 이용한 표층류 관측 ... 97
• 나. 표면 유출유 추적부이 ... 100
• 다. SAR 정보 이용 원격탐지기술 ... 100
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 101
• 2. 예측 모델망 ... 102
• 가. 기상정보 산출 및 제공시스템 ... 102
• 나. 해수순환 예측 모델링 ... 106
• 다. 유출유 거동 예측 모델 및 방제 대응시스템 ... 111
• 라. 그리드 기술 기반의 재난 대응시스템 ... 113
• 3. 오염진단·평가 및 정화기술 분야 ... 116
• 가. 오염진단·평가 기술 ... 116
• 나. 정화 기술 ... 117
• 4. 선박파손부 긴급봉쇄장치 개발 분야 ... 118
• 제2절 연구결과가 국내·외 기술개발현황에서 차지하는 위치 ... 122
• 1. 원격관측망 분야 ... 122
• 가. HF radar ... 122
• 나. 표면 유출유 추적부이 ... 122
• 다. SAR 위성을 이용한 원격관측 ... 122
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 123
• 2. 예측 모델망 분야 ... 123
• 가. 해양기상 모델 ... 123
• 나. 해수순환 예측 모델링 ... 124
• 다. 첨단 유출유 거동 예측 모델 ... 124
• 라. 그리드 기술 기반의 실시간 해양 오염 예측 시스템 구축 ... 124
• 3. 오염진단·평가 및 정화기술 분야 ... 125
• 가. 진단 평가 기술 ... 125
• 나. 정화기술 ... 125
• 4. 선박파손부 긴급봉쇄장치 개발 분야 ... 126
• 제3장 연구수행 내용 및 결과 ... 129
• 제1절 연구수행 방법 및 내용 ... 131
• 1. 원격관측망 분야 ... 131
• 가. HF radar 이용 표층류 관측 ... 131
• 나. 표면 유출유 추적부이 ... 145
• 다. SAR 위성을 이용한 기름오염 감시 ... 149
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 152
• 2. 예측 모델망 분야 ... 162
• 가. 해양기상 정보산출 및 제공시스템 ... 162
• 나. 해수순환 예측 모델링 ... 168
• 다. 첨단 유출유 거동 예측 시스템 개발 ... 190
• 라. 그리드 기술 기반의 실시간 해양 오염 예측 시스템 구축 ... 212
• 3. 오염 진단·평가, 정화 기술 분야 ... 213
• 가. 오염진단 평가 ... 213
• 나. 정화기술 ... 235
• 4. 선박파손부 긴급 봉쇄 및 잔존유 제거 장치 분야 ... 239
• 가. 파공 사례 ... 239
• 나. 파공봉쇄장치 ... 244
• 다. 잔존유 제거장치 ... 245
• 제2절 연구결과 ... 246
• 1. 원격관측망 구축 분야 ... 246
• 가. HF radar 관측 ... 246
• 나. 표면 유출유 추적부이 ... 248
• 다. SAR 위성정보를 이용한 유출유 감시 ... 256
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 281
• 2. 예측 모델망 구축 ... 283
• 가. 해양기상 정보산출 및 제공 시스템 ... 283
• 나. 해수순환 예측 시스템 ... 291
• 다. 첨단 유출유 거동 예측 시스템 개발 ... 338
• 라. 그리드 서비스 환경 개발 ... 355
• 3. 오염 진단·평가, 정화 기술 분야 ... 376
• 가. 오염진단 평가 ... 376
• 나. 정화기술 ... 418
• 4. 선박 파손부 긴급봉쇄 및 잔존유 제거 기술 분야 ... 434
• 가. 기술 개발 과정 및 이론 ... 434
• 나. 파공봉쇄장치 시작품 제작 ... 437
• 다. 적용 사례 ... 442
• 라. 본 연구에서 출원한 특허 ... 453
• 제4장 목표달성도 및 관련분야에의 기여도 ... 457
• 제1절 연차별 세부연구목표 및 평가의 착안점 ... 459
• 제2절 연구목표의 달성도 ... 460
• 1. 원격관측망 구축 분야 ... 460
• 가. HF radar 관측 ... 460
• 나. 표면 유출유 추적부이 ... 461
• 다. SAR 위성정보를 이용한 유출유 모니터링 ... 461
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 461
• 2. 예측 모델망 구축 분야 ... 462
• 가. 기상정보 산출 및 제공시스템 ... 462
• 나. 해수순환 예측 시스템 ... 462
• 다. 첨단 유출유 거동 예측 모델 개발 ... 463
• 라. 그리드 기술 기반의 실시간 해양 오염 예측 시스템 구축 ... 463
• 3. 오염진단·평가 및 정화기술 분야 ... 464
• 가. 오염 진단 평가 기술 ... 464
• 나. 오염 암반 정화기술 개발 ... 466
• 4. 선박 파손부 긴급봉쇄 및 잔존유 제거 기술 분야 ... 466
• 제3절 관련분야 기술발전에의 기여도 ... 467
• 1. 원격관측망 구축 분야 ... 467
• 가. HF radar 관측 ... 467
• 나. 표면 유출유 추적부이 ... 467
• 다. SAR 위성정보를 이용한 유출유 감시 기술 ... 468
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 468
• 2. 예측 모델망 구축 분야 ... 468
• 가. 기상정보 산출 및 제공시스템 ... 468
• 나. 해수순환 예측 모델링 ... 469
• 다. 첨단 유출유 거동 예측 모델 개발 ... 469
• 3. 오염진단·평가 및 정화기술 분야 ... 470
• 가. 오염 진단 평가 기술 ... 470
• 나. 오염 암반 정화기술 개발 ... 471
• 4. 선박 파손부 긴급봉쇄 및 잔존유 제거 기술 분야 ... 471
• 가. 기름유출 방지 기술 발전에의 기여도 ... 471
• 나. 선박의 침수, 침몰 방지 기술 발전에의 기여도 ... 472
• 제5장 연구결과의 활용계획 ... 473
• 제1절 연구결과의 활용계획 ... 475
• 1. 원격관측망 구축 분야 ... 475
• 가. HF radar 관측 ... 475
• 나. 표면 유출유 추적부이 ... 475
• 다. SAR 위성 정보를 이용한 유출유 감시 ... 475
• 라. 선박레이더를 이용한 유출유 추적기법 개발 ... 476
• 2. 예측 모델망 구축 분야 ... 476
• 가. 기상정보 산출 및 제공시스템 ... 476
• 나. 해수순환 예측 모델링 ... 476
• 다. 첨단 유출유 거동 예측 모델 개발 ... 477
• 3. 오염진단·평가 및 정화기술 분야 ... 477
• 가. 오염 진단 평가 기술 ... 477
• 나. 오염암반 정화 기술 ... 478
• 4. 선박 파손부 긴급봉쇄 및 잔존유 제거 기술 분야 ... 478
• 가. 선박 파손부 긴급봉쇄장치 및 관련 기술 ... 478
• 제2절 2단계 연구계획 ... 478
• 1. 원격관측망 구축 분야 ... 478
• 가. HF radar 관측 ... 478
• 나. 표면 유출유 추적부이 ... 479
• 다. SAR 위성 정보를 이용한 유출유 감시 기술 ... 479
• 라. 선박레이더를 이용한 유출유 탐지 시스템 개발 ... 479
• 2. 예측 모델망 구축 분야 ... 479
• 가. 해양기상 정보 시스템 ... 479
• 나. 해수순환 예측 시스템 ... 480
• 다. 3차원 유출유 거동 예측 모델 기반 해양사고 대응 의사결정 지원 기술 개발 ... 480
• 라. 클라우드 환경 기반의 실시간 해양 오염 예측 시스템 구축 ... 481
• 3. 오염진단·평가 및 정화기술 분야 ... 482
• 가. 오염 진단·평가 기술 ... 482
• 나. 오염암반 정화 기술 ... 483
• 4. 선박 파손부 긴급봉쇄 및 잔존유 제거 기술 분야 ... 483
• 가. 원격이동 시스템 개발 ... 483
• 나. 형식 승인 추진 ... 483
• 다. 국제적 활용 기반 구축 ... 484
• 제6장 연구과정에서 수집한 해외과학기술정보 ... 485
• 1. 원격관측망 구축 분야 ... 487
• 가. 해류관측 기술관련 정보 ... 487
• 나. SAR 위성정보를 이용한 유출유 감시 기술 ... 487
• 2. 예측 모델망 분야 ... 488
• 가. 순환 모델링관련 정보 ... 488
• 나. 유출유 거동 예측 모델링관련 정보 ... 488
• 3. 오염 진단 평가 및 정화 기술관련 정보 ... 490
• 4. 선박 파손부 긴급봉쇄장치 관련 정보 ... 491
• 제7장 참고문헌 ... 493
• 부록 ... 509
• 부록 1. 제주해협 현장관측 조사 ... 511
• 부록 2. 표면 유출유 추적부이 모니터링 어플리케이션의 설치 및 사용법 ... 519
• 부록 3. 우크라이나 IMMSP와의 공동 연구 성과 ... 524
• 부록 4. 2011년 일본 동북태평양지진 현지조사 보고 ... 528
• 부록 5. NAP 참여연구원 ... 546
• 끝페이지 ... 546