본 연구에서는 형광측정기법을 사용하여 태안반도 인근 8지점의 표층 해수 내 미세플라스틱 정량분포를 조사하였다. 연구결과 미세플라스틱의 검출범위는 0~360.5 particles/l (평균 149.7 ± 46.0 particles/l)로 나타났다. 하지만 해양환경 내 미세플라스틱의 정량분석방법이 표준화되지 않아 타 연구결과와 직접비교 하는 것이 불가능한 상황이다. 본 연구결과 검출된 미세플라스 틱을 크기별로 분류하면 < 50 μm 크기가 우점하지만, St. 3의 경우 > 500 μm이 25.6%를 차 지하여 지역별로 우점하는 미세플라스틱의 크기에 차이가 나타난다. 또한 채집지역, 저질의 종 류, 검출되는 플라스틱 크기에 따른 미세플라스틱의 검출량 비교에도 뚜렷한 상관관계를 가지 는 요인을 확인할 수 없었다. 이는 플라스틱의 재질에 따른 물리 · 화학적 특성, 해양의 동적 조건(해류, 바람, 파도, 조류 등), 지질학적 특성(지형, 경사 등), 연안 생물을 포함한 저질의 구성 및 특성, 상호작용, 인간활동(어업, 개발, 관광 등), 기상조건(홍수, 강우 등)과 같은 다양한 요인 이 미세플라스틱의 거동에 영향을 주기 때문이다. 그러므로 향후 정량분석방법 표준화 및 환 경요인에 대한 분석이 수반된 미세플라스틱 모니터링 기초연구가 필요한 상황이다.
During and after the construction of LILW disposal facilities, the decrease of groundwater head potential has been monitored. In addition, an increase of the electrical conductivity (EC) has been observed in several monitoring wells installed along the coastal coastline. Monitoring activity for groundwater head potential and hydrogeochemical properties is important to reduce the uncertainty in the evaluation of groundwater flow characteristics. However, the data observed in the monitoring wells are spatial point data, so there is a limit to the dimension. Several researchers evaluated groundwater head potential changes and seawater intrusion (SWI) potential for disposal sites using groundwater flow modeling. In case of groundwater flow modeling results for SWI, there is a spatial limit in directly comparing the EC observed in the monitoring wells with the modeling results. In a recent study, it was confirmed that the response of the long-range ground penetraiing radar (GPR) system was severely attenuated in the presence of saline groundwater. In order to reduce the spatial constraint of the groundwater monitoring wells for SWI, the characteristics of SWI within the disposal facility site by using the the results of a recent study of the long-range GPR system were investigated and evaluated in this study.
This study assessed the levels of water qualities and microbials contamination of inland olive flounder farms in Jeju in the summers from 2015 to 2017. Three farms (A-C) located in a concentrated area using mixing coastal seawater and underground seawater and one farm (D) located in an independent area using only coastal seawater were selected. Total ammonia nitrogen (TAN) reached a maximum of 0.898 ± 1.024 mg/L as N in the coastal seawater of A-C, which was close to the limit of the water quality management goal of the fish farm. TAN in the influent from A-C was up to three times higher than that of D, so that the discharged water did not spread to a wide range area along the coast and continued to affect the influent. TAN of the effluent in A-C increased by 2.7-4.6 times compared to the influent, resulting in serious self-pollution in the flounder farm. Heterotrophic marine bacteria in the influent of A-C was about 600 times higher than D, and the discharge of A-C was increased by about 30 times compared to the influent.
Seasonal characteristics of water and sediment qualities and potential effects of the freshwater discharge from a small tide embankment interior in a coastal area in Goheung county were investigated from May to September in 2012. Chemical oxygen demand values (COD) were mostly higher than 2 mg/L in summer ebb tide, which exceed the standard value of water quality criteria II of acceptable level for aquaculture activities. Nitrogen and phosphorus were found as the limiting nutrients for algae growth in summer and fall and in spring, respectively. Nitrogen was the limiting nutrient for diatom growth in the whole studied period. The sudden high values of COD, ammonia, dissolved inorganic nitrogen (DIN), dissolved inorganic phosphorus (DIP) were found in water sample collected from station 5 which located in front of the tide embankment sluice gate during spring ebb tide. The freshwater discharge form the tide embankment interior maybe affected the survey areas during a short time interval. Mean values of eutrophication index of the surveyed coastal region in spring, summer and fall were all bigger than 1. Water quality was mostly considered at level II which acceptable for aquaculture activities. Sediment quality in this study was generally in the range of standard for fisheries environment.
The aim of this study was to investigate the effects of environmental factors such as temperature, salinity, turbidity and pH on the growth of pathogenic Vibrios. In this study, we was obtained the samples from 2 different sites of the Incheon coastal area between January 2012 and December 2012. The water temperature in August and September was the high. the Incheon port changes the width of a small, wherease in the case of Hanjin harbor of changes of larger width. Salinity and turbidity showed significant differences, whereas temperature and hydrogen ion concentration was not significant. Pathogenic vibrios was determined using the real-time PCR method. Pathogenic vibrios in the Incheon port and Hanjin harbor were detected in 11 samples (91.67%) and 9 samples (75.0%) of Vibrio cholerae, 7 samples (58.3%) and 6 samples (50.0%) of V. vulnificus, 10 samples (83.3%) and 12 samples (100.0%) of V. parahaemolyticus, respectively. Pathogenic Vibrio bacteria were the highest at 26.8℃ of seawater in August. Quantitative results were the following: 102 cell/㎖ in Vibrio cholerae, 7.876 cell/㎖ in V. vulnificus, and 503.4 cell/㎖ in V. parahaemolyticus, respectively. The enumeration of pathogenic vibrios showed a positive correlation with temperature and pH, but was negatively correlated with salinity and turbidity.
2000년대 초반부터 연안준설 사업의 수요가 크게 증가하였고, 기타 연안개발 사업과도 중첩되어 준설토의 발생량은 지속적으로 증가하고 있다. 이로 인해 주변해역에 대한 환경 영향이 심화될 수밖에 없는 상황에서, 2011년 제출된 해역이용협의서 중 준설이 포함된 사업의 해수 및 해저 퇴적물에 대한 해양환경영향평가 현황을 파악하였다. 해양환경영향평가 항목 중 일반 항목들의 조사 비율은 대체로 높은 반면, 중금속 등 유해 물질의 경우에는 세부항목들 간 조사 비율 편차가 크게 나타났다. 한편 중금속 분석 시 협의서 작성 지침에 따른 전처리 과정(완전 분해)과 분석 방법이 제대로 수행되지 않았다. 또한 작성 지침에 명시되어 있지는 않지만, 결과값에 대해 신뢰도 확보를 위한 검증(회수율 및 검출한계 산정) 수행 현황도 매우 미흡한 것으로 파악되었다. 이로 인해 연안 준설 및 개발에 따른 주변 해양환경영향평가가 부실하게 진행되고 있는 것으로 나타났다. 향후 해양 수질 및 퇴적물 환경에 대해 보다 엄정한 평가와 진단을 위해서는 협의서 작성에 관한 세부 지침의 보완이 요구되며, 해역이용협의 제도의 개선을 통해 정확한 해양환경영향평가가 수행되도록 협의서 작성지침의 준수 의무를 강화할 필요가 있는 것으로 판단되었다.
Heavy metal concentration of Fe, Zn, Cu, Cd and Pb were analysed from seaweeds (Ulva pertusa, Sargassum thunbergii, Caulacanthus okamurae), sediments and seawater at the two experimental sites of Daebul and Sabjin industrial complex in Mokpo coastal area
Seawater temperature, salinity, dissolved oxygen, nutrients and chlorophyll-a have been studied around Hamduck in the northern part of Cheju Island during July, 1989-July, 1990. In the surface water ranges of water temperature, salinity, dissolved oxygen, nitrate, phospate, silicate and chlorophyll-a have been 13.7-26.5℃, 28.51-34.37‰, 4.47-7.14㎖/ℓ, ND-15.42㎍-at/ℓ, ND-1.47㎍-at/ℓ, 2.33-24.1㎍-at/ℓ, and 0.02-2.24㎎/㎥, respectively. Yearly mean values of the near surface waters(0m-10m)at station 6 show high temperature, nitrate, chlorophyll-a, while the values of dissolved oxygen, phosphate, and silicate were low compared with the other stations. The vertical profiles are likely to show the possibility of upwelling in October and tidal front in July, suggesting high productivity of phytoplankton around St.6. N1P ratio varies from 35 inshore to 15 offshore and from 45 in July to 15 in Ferbruary. These variation patterns are similar to those of water temperature.
본 연구에서는 해수-담수-해안대수층의 비선형 상호작용을 직접 해석할 있는 PBM(Porous Body Model) 기반의 3차원 N-S Solver인 LES-WASS-3D ver 2.0을 적용하며, 해안대수층의 해수침투모의를 수행하였다. 이와 같은 N-S Solver를 적용한 해안대수층의 해수침투모의는 국내 최초 수행되는 것일 뿐만 아니라, 국외적으로도 찾아보기 어려운 새로운 수치해석방법이라고 할 수 있다. 먼저 적용하는 수치모델을 검증하기 위하여 해안대수층의 해수-담수 경계면에 관한 수리모형실험결과와 비교·검토 하여 수치모델의 타당성 및 유효성을 확인하였다. 그리고 해수위 및 지하수위 변화를 고려한 해안대수층 내의 해수침투모의를 수행하여 해수위-지하수위 차와 해수위의 비(△h/h)의 증가에 따른 해안대수층 내의 유동장 그리고 해수-담수 경계면 분포 특성에 관하여 논의하였다. 또한 기존의 비확산 수치모델에서 도출할 수 없었던, △h/h에 따른 해안대수층 내의 연직 염분농도로 부터 해수침투 특성을 파악하였으며, 최종적으로 지표화 할 수 있는 △h/h가 해안대수층 내의 해수침투거리에 미치는 영향에 대하여 분석하였다. 이 결과로부터 △h/h가 작을수록 해안대수층 내의 해수침투가 약해지는 메커니즘을 이해할 수 있었다.
Polycyclic aromatic hydrocarbons (PAHs) were investigated in seawater and marine sediment from Anmyundo coastal area after oil spill. The concentrations of total PAHs in surface and bottom of seawater at August were 31.1 to 142.6 ng/L and 5.9 to 50.9 ng/L in August and November, respectively. The concentrations of PAHs in sediment were 21.0 to 102.9 ng/g D.W. and 32.3 to 57.4 ng/g D.W. in August and November, respectively. PAHs concentrations in seawater and sediment in August were higher than those in November about 2.5 and 1.4 times, respectively. Diagnostic ratio (PhA/AnT and FluA/Pyr) were investigated to identify source of PAHs in seawater and sediment. The PAHs in seawater originated from pyrolytic source and those in sediment originated from pyrolytic and petrogenic source. The glass, wood and coal origin was higher than petroleum origin on the combustion origin of PAHs in seawater and sediment. The seawater of Anmyundo costal area recovered from oil spill, but the sediments of that were weakly influenced by oil spill until now. Because this area is developed many fishing grounds, demanded Long Term Environmental Monitoring Program (LTEMP). The concentrations of PAHs on depth of sediments were investigated at station 8 and 10. The concentrations of PAHs were decreased with increasing depth.