메뉴 건너뛰기
.. 내서재 .. 알림
소속 기관/학교 인증
인증하면 논문, 학술자료 등을  무료로 열람할 수 있어요.
한국대학교, 누리자동차, 시립도서관 등 나의 기관을 확인해보세요
(국내 대학 90% 이상 구독 중)
로그인 회원가입 고객센터 ENG
주제분류

추천
검색

논문 기본 정보

자료유형
학위논문
저자정보

김민아 (충남대학교, 忠南大學校 大學院)

지도교수
崔在鎔
발행연도
2013
저작권
충남대학교 논문은 저작권에 의해 보호받습니다.

이용수1

표지
AI에게 요청하기
추천
검색

이 논문의 연구 히스토리 (2)

초록· 키워드

오류제보하기
ABSTRACT*

Due to Korea’s rapid economic growth, forest landscapes along the urban/rural interface are increasingly under threat of urban sprawl and other unplanned development. Particularly, the patterns and trajectories of the cumulative changes cause forest fragmentations and permanent loss of forestland in the region as well as habitat quality and thus biological diversity. These cumulated negative impacts are ultimately threatening our sustainability in life. Therefore, the primary mission has been to reduce global forest fragmentation, restore forests/ecosystem to healthy conditions, and provide the optimal ecological benefits possible.

According to the Management of Mountainous Districts Act, Ecosystem management and the related field of landscape ecology required “Forestland Primary Assessment System” since 2011 in order to look at a variety of spatial scales of developments in the field of landscape ecology, and to regulate any kind of indiscriminate development processes. Forestland Primary Assessment System advises to get the forest inspected by an expert when proceeding the restoration of forest land use conversion or temporary use of forest land. In regards to the enforcement of Forestland Primary Assessment System, Korea Forest Research Institute emphasized on the importance of habitat space, the natural forest vegetation and animals, wild habitats conservation, and most importantly, terrestrial biodiversity. Korea Forest Research Institute has proceeded a standard reference research including “wildlife habitats fragmentation” (2011) in the assessment components to determine the condition of forestlands. Despite the fact that it is crucial for Forestland Primary Assessment System to attain an inquiry regarding environmental factors such as “wildlife habitats fragmentation/landscape metric transformation” that include “biodiversity” and “fragmentation” factors, current Forestland Primary Assessment System only concentrates on general evaluation components such as trees accumulation, altitude/longitude of landscapes, natural and aesthetic values of the forest, and natural disaster management (Management of Mountainous Districts Act, enforcement Item 20, Clause 3).

The general purpose of this study was to analyze impacts of the forest fragmentation caused by development project, examine the applicability of landscape indicator through Forestland Primary Assessment System, and compare before and after impacts of areal and linear development. Through this process, the ultimate intention is to capture the impacts of forest fragmentation and its significance, and bring up the question of the current Forestland Primary Assessment System and its necessary improvement which we must consider.

Specifically, this study aims for the significant impacts of development industry on surrounding forest ecosystem. In order to analyze the environmental consequences on forest landscape fragmentation caused by golf course development and road construction, we employed FRAGSTATS model, the program for analyzing fragmentation. To conduct a quantitative analysis study of fragmentation due to development industry actions, we applied landscape index such as LPI (Largest Patch Index), NP (Number of Patches), LSI (Landscape Shape Index), PD (Patch Density), CPLAND (Percentage of Landscape), and TCA (Total Core Area) that are relevant to the core area.

As the results of golf course development’s impact analysis, AREA (patch area) decreased while the number of patches increased as well as LSI (Landscape Shape Index) that presents patch density and complexity. In the core region, patch area decreased as a big forest patch got divided into different patches. After examining landscape ecological impacts of road construction, areal development project showed not much different appearance as before. However, landscape index outcomes displayed that there was a prominent gap between before and after impacts specifically including patch area, and number of patches indexes.

Findings suggested that since development industry actions has occurred; landscape ecological integrity has declined while biodiversity loss in terrestrial ecosystems increased. Also, the appearance change of both areal and linear development roughly stayed equal, although linear development project’s before and after landscape index differed by its numbers. This particular result of increase in linear development proved that linear development projects caused more fragmentations than areal development projects. Moreover, linear development projects have a tendency of passing through places such as forests, swamps, and rivers, which could possibly disrupt human life condition unlike areal development projects, and cause significant negative impacts on natural environment. Nevertheless, it would be possible to collect an objective and accurate impact analysis of forest structure and its fragmentations by using LPI, NP, LSI, PD, CPLAND, and TCA indexes. Besides forest patch fragmentations, it appeared that if we could conduct research studies that include variety of plant and animal species, and improve on fragmentations analysis regarding landscape metric, the possibility of accurately implementing Forestland Primary Assessment System would considerably increase.

All in all, the analysis of fragmentations caused by development industry actions directly displayed biodiversity losses in ecosystem such as the decrease of forest area and connection function, and the creation of edges. We must expand efforts to define and develop protocols for sustainable forest management, Forestland Primary Assessment System, and take account of future consequences in order to minimize harmful impacts and fragmentations due to excessive development industry actions, and finally enhance a healthy terrestrial biodiversity.

목차

Ⅰ. 서 론 1
1. 연구배경 및 목적 1
2. 연구범위 및 흐름 5
Ⅱ. 관련 이론 및 선행연구 고찰 8
1. 산지전용타당성조사제도에 관한 연구 8
1.1 산지전용 8
1.2 산지전용타당성조사 8
1.3 산지전용타당성 조사를 위한 기준 및 지표 체계 10
2. 산림파편화 12
2.1 산림파편화와 생태계영향 15
2.2 산림파편화와 경관변화 18
Ⅲ. 연구내용 및 방법 22
1. 경관 지수 선정 22
2. FRAGSTATS 모델의 적용 26
Ⅳ. 분석 및 결과 29
1. 면적개발사업 대상지 29
1.1 패치의 크기/밀도/가장자리 (LPI/NP) 31
1.2 패치 형태 (LSI/PD) 32
1.3 핵심구역 (CPLAND/TCA) 33
2. 선형개발사업 대상지 35
2.1 패치의 크기/밀도/가장자리 (LPI/NP) 36
2.2 패치 형태 (LSI/PD) 36
2.3 핵심구역 (CPLAND/TCA) 37
3. 면적사업 및 선형사업대상지 비교 38
3.1 패치의 크기밀도/가장자리(LPI/NP) 38
3.2 패치 형태 (LSI/PD) 40
3.3 핵심구역 (CPLAND/TCA) 41
Ⅴ. 결론 44
1. 연구의 주요 결과 44
2. 연구의 한계 및 향후 과제 46
참고문헌 47
ABSTRACT 60

최근 본 자료

전체보기

댓글(0)

0