Fishing dredge in Jeollabuk-do began to become widespread in the 1960s and has continued to catch diverse kinds of shellfish in the productive fishing grounds around Dongjin River, Mangyeong River and Geum River estuaries. Since the 1970s, the construction of various large-scale industrial complex and the implementation of Saemangeum reclamation project have resulted in a decrease in main fishing areas and a sharp decline in shellfish production. As a result, dredge fishery has faced many difficulties. Dredge fishery in Jeollabuk-do is carried out with a total of 30 fishing permits as of 2016. Surf clams, hen clams, bladder moon snails, and common orient clams were mainly caught before the construction of Saemangeum dike while comb pen shells, purple whelks and ark shells are mainly caught afterwards. Inside the Saemangeum dike, most fish species have disappeared due to low water level and low salinity, and littleneck clams are caught using a jet pump type of fishing dredge. Outside the dike, the diversity of shellfish species has been reduced; comb pen shells are mainly caught. In this process, a lot of friction occurs due to the use of a reformatted dredge. Therefore, a lot of research needs to be conducted in the near future.

The maximum sustained yield ( ) of shellfish caught through dredge fishery was 7,250 to 7,490 MT from 1990 to 1999, which was not affected by the construction of the Saemangeum Dike. The MSY from 2000 to 2016, under the influence of the dike, was 1,716 to 1,776 MT when the total annual fish catch was 1,000 MT or more, and 289 to 336 MT when it was less than 1,000 MT. The construction of the Saemangeum Dike led to a decrease in the catch volume of the offshore dredge fishery in Jeollabuk-do, to 4.2 to 23.7% of that before its construction. The allowable biological catch () was estimated to be 313 to 1,532 MT per year, which was about 72.3 to 94.3% less than before the construction of Saemangeum Dike. Currently, the dredge fishery in Jeollabuk-do relies on comb pen shells. For fishery management, the catch per vessel should be set at 51.0 MT/year or less, and the number of fishing vessels should be reduced to 22 as quickly as possible. Besides, in the long term, the number of current fishing vessels should be reduced to less than half in consideration of the comb pen shell collecting period in Jeollabuk-do.

아산만 인근해역은 최근 20여년 넘게 실시된 각종 방조제 공사가 저서동물의 군집구조에 영향을 주는 것으로 알려지고 있지만, 이에 대한 연구는 충분치 않다. 그러므로 본 연구에서는 화옹방조제 건설 이후 아산만 대형저서동물의 군집구조에 영향을 주는 환경요인을 분석하였다. 대형저서동물 채집은 2007년 8월과 2008년 2월에 아산만 주변 해역 22개의 정점에서, 스미스 맥킨타이어 그랩(Smith McIntyre Grab, 표면 면적: 0.1m2)을 이

서남해에 위치한 영산강 하구는 1981년 12월에 하구언이 건설되기 전까지 전형적인 하구의 모습을 보였다. 하지만 하구언이 건설되면서 수질뿐만 아니라 식물플랑크톤이나 동물플랑크톤과 같은 부유생물들의 생물상들도 변화를 나타낼 것으로 예상된다. 따라서 기존에 보고된 자료와 최근 채집한 현장조사 자료를 토대로 식물플랑크톤 군집과 식물플랑크톤 관련 환경인자들의 변화를 조사하였다. 하구언 건설 직후(1984년)의 환경 자료와 최근 자료를 비교 검토한 결과, 담수

금강하구둑 축조 전 후의 조석변화를 알기위하여 금강하구의 조류조화상수 및 비조화상수를 분석하였다. 그 결과, 하구둑 축조 후에 조화상수 및 비조화상수가 증가하였다. 또한 연도별 해도자료를 이용하여 구간별 수심변화를 분석하였다. 그 결과 남 북측도류제 사이의 수로에서는 세굴이 발생하였다. 그리고 군산외항에서 하구둑까지의 수로에서는 퇴적이 발생하였다. 조석변화는 건설과 준설, 금강하구둑의 수문닫힘의 영향으로 판단된다 그리고 수심변화는 금강하구둑 건설과

The purpose of this study is the assessment of changes in the leisure patterns of users of the Eulsook-do before and after the estuary dike construction. The following survey research method was conducted to implement the study, sampling by age was carried out selectively and randomly alike. A total of 319 persons were chosen for final analysis, excluding questionnaires answered found to be inappropriate. To measure the image of the lower Nakdong River around the Eulsook-do, with advice sought from experts, researchers, through several pilot tests, developed a 24-item semantic differential scale(SDS) that has two bi-polar adjectives at each end Study of the pre- and post- construction images of the Eulsook-do located on the coast of Busan suggests the dike construction has brought about negative changes in the Eulsook-do's overall image. There can be two alternatives for improving the negative image: restoration and development.