본 연구는 중부지방에서 각종 기후인자의 영향을 명확히 반영하여 중부지방의 날씨 및 기후 특성을 잘 나타내는, 탁월일기 및 강수현상의 하계 순별 출현 다소(강수 없음, 0.1-10.0mm/일, 10.1-30.0mm/일, 30.1mm 이상/일)와 그 변화에 대해, 정보이론을 이용하여 일기엔트로피와 정보비를 추출하고 응용하여, 그 공간 스케일의 시간적 변동을 살핀다. 그리고 본 연구는 하계 순의 중부 지방의 25개 관측 지점별 일기 및 기후 대표성의 특성을 규명하고 공간적 질서를 밝혀 일기예보 및 핵심 기후지역(기후대표성) 설정을 시도한 것이다. 그 결과 최대 일기엔트로피(제1위: 춘천, 1.870bits, 7월 하순)는 대부분 8월 초순에 나타나고, 최소 일기엔트로피(제1위: 강화, 0.960 bits, 9월 중순)는 6월 초순과 9월 하순에 나타난다.15개 기준지점(속초, 철원, 대관령, 춘천, 강릉, 서울, 인천, 원주, 수원, 충주, 서산, 청주, 대전, 보령 및 부여)의 정보비 분포와 일기대표성의 특성은 주로 9월 중순(제1위 충주 기준 시 청주 0.75, 6월 초순)에 가장 크며, 7월 하순(제1위 보령 기준 시 대관령 0.06, 7월 하순)에 가장 작다는 것을 밝혔다. 그리고 중부지방의 일기예보 및 기후대표성(기후지역)을 나타내는 핵심지역은 부여-인천-강릉지역을 잇는 삼각형내의 중부 내륙지방이 해당됨을 밝혔다.

The selection of land for fishing village development project, and the standard used to classify fishing villages has been determined based on the guidelines developed by fishing village cooperatives. The approach fishing village cooperatives follows is likely to classify fishing villages without first reflecting on the overall development environment of the region, such as other industries and workers in the area. It also acts as a barrier for business promotion or evaluation, because the cooperatives do not match the administrative districts, which are the units of administration, and the main policy enforcement agent in regional development. Against this background, this study aimed to identify categories to situate the development direction, as well as the size and distribution of fishing villages based on eup, myeon, and dong administrative units as defined by the Fishing Villages and Fishery Harbors Act. This study was based on the Census of Agriculture, Forestry, and Fisheries of 2010, and analyzed 826 eups, myeon, and dongs with fishery households using the principal component analysis, and 2-Step cluster analysis methods. Therefore, 95% of the variance was explained using the covariance matrix for types of fishing villages, but it was analyzed as one component focusing on the number and ratio of fishery households, and used the cluster-type analysis, which focused on the sizes of fishing villages. The clusters were categorized into three types: (1) the development type based on the number of fishermen in the eups, myeons and dongs was analyzed as village size (682); (2) administrative district size (121); and (3) total eups, myeons and dongs (23), which revealed that the size of most fishing villages was small. We could explain 73% of the variance using the correlation coefficient matrix, which was divided into three types according to the three principal component scores, namely fishery household power, fishery industry power, and fishing village tourism power. Most fishing villages did not have a clear development direction because all business areas within the region were diversified, and 552 regions could be categorized under the harmonious development type, which is in need of balanced development. The fishery industry type typified by industrial strength included 159 regions in need of an approach based on industrialization of fishery product processing. Specialized production areas, which specialized in producing fishery products, were 115 regions with a high percentage of fishermen. The analysis results indicated that various situations in terms of size and development of fishing villages existed. However, because several regions exist in the form of small village units, it was necessary to approach the project in a manner that directed the diversification of regional development projects, such as places for local residents to relax or enjoy tourism experiences within the region, while considering the overall conditions of the relevant eups, myeons, and dongs. Reinforcement of individual support for fishermen based on the Fisheries Act must take precedence over providing support for fishermen through regional development. In addition, it is necessary to approach the development of fishing villages by focusing on industrializing the processing techniques of fishery products. Areas specialized in the production of fishery products are required to consider the facilities for fisheries production, and must make efforts to increase fishery resources, such as releasing fry.