[논문]지리산국립공원 심원계곡 생태경관 복원공사지역 식생 변화

정태준; 김연경; 김영진; 정명희; 박경희; 신창근; 박선홍; 김영선

doi:10.13047/kjee.2021.35.3.294

[국내논문] 지리산국립공원 심원계곡 생태경관 복원공사지역 식생 변화
A Change of Vegetation at the Ecological Restoration Area of Simwon Valley in Jirisan National Park 원문보기

한국환경생태학회지 = Korean journal of environment and ecology, v.35 no.3, 2021년, pp.294 - 304

정태준 (상지대학교 대학원 응용식물과학과) , 김연경 (한그루 27) , 김영진 (목포대학교 대학원 조경학과) , 정명희 (경상대학교 대학원 산림자원학과) , 박경희 (목포대학교 대학원 조경학과) , 신창근 (지리산국립공원 전남사무소) , 박선홍 (지리산국립공원 전남사무소) , 김영선 ((사)한백생태연구소)

초록
AI-Helper

본 연구는 지리산국립공원 심원계곡 생태경관 복원공사지역의 모니터링 결과를 분석하여 체계적인 복원관리를 도모할 수 있는 기초자료를 확보하는데 그 목적이 있다. 복원사업이 완료된 2017년도에 식생 모니터링을 위한 조사구 12개소와 대조구 4개소를 설치하였고, 2017년과 2020년의 상대우점치, 종다양도지수, 유사도 등의 변화를 분석하였다. 복원사업 시 수목이 식재되었던 조사구는 종다양도지수가 0~1.4552로 나타났고, 대조구와의 유사도지수에서는 1개 조사구가 1.32%로 분석된 것을 제외하고 모두 0%로 나타났다. 조사구의 종다양도지수 및 유사도지수가 매우 낮은 것은 복원사업 시 식재된 수목이 고사하거나 멧돼지 피해, 유수에 의한 침식으로 유실되는 등의 영향으로 판단되었다. 반면 복원사업 시 수목이 식재되지 않은 미식재 조사구는 종다양도지수가 0.9538~2.3222로 나타났고, 유사도지수는 최대 8.33%까지 분석되었다. 국립공원 생태경관 복원공사지역의 복원 공법 개발을 위한 장기 모니터링과, 미식재 조사구의 천이과정을 분석하는 지속적인 연구가 필요하다.

Abstract ▼ AI-Helper

This study aims to obtain basic data for systematic restoration by analyzing the monitoring results of the Shimwon Valley Ecological Landscape Restoration Project area in Jirisan National Park. In 2017, when the restoration project was completed, 12 monitoring plots and 4 control plots were installed for vegetation monitoring, and changes in the relative dominance, species diversity index and similarity between 2017 and 2020 were analyzed. The species diversity index of the surveyed areas where trees were planted during the restoration project was 0-1.4552, and the similarity index with the control group was 0% except for one survey area at 1.32%. The very low species diversity index and similarity index in the survey areas were attributed to the loss of trees planted during the restoration project due to death, damage by wild boars, or erosion by running water. On the other hand, the species diversity index was 0.9538-2.3222 in the monitoring plot where no tree was planted, and the similarity index was analyzed to be as high as 8.33%. It is necessary to continue the long-term monitoring for the development of ecological landscape restoration methods in the national park and analysis of the succession in monitoring plots where no trees were planted.

주제어

표/그림 (11)

그림 Figure 1. Location map of monitoring and control plots at ecological restoration area of Simwon valley in Jirisan National Park.
표 Table 1. Size and number of monitoring and Control plots at Ecological Restoration area of Simwon Valley in Jirisan National Park
표 Table 2. General description of monitoring plots at ecological restoration area of Simwon valley in Jirisan National Park
표 Table 3. The flora of monitoring and control plots at ecological restoration area of Simwon valley in Jirisan National Park
표 Table 2. (Continued)
표 Table 4. Relative Importance Percentage of monitoring and control plots at ecological restoration area of Simwon valley in Jirisan National Park
표 Table 4. (continued)
그림 Figure 2. Comparison of changes in species diversity index of monitoring and control plots(2017-2020).
표 Table 5. Species diversity index of monitoring and control plots at ecological restoration area of Simwon valley in Jirisan National Park
표 Table 6. Similarity index of monitoring and control plots at ecological restoration area of Simwon valley in Jirisan National Park
표 Table 7. Comparison of changes in similarity index of monitoring and control plots(2017-2020)

참고문헌 (28)

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상세보기
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상세보기
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표제어: PCR

동의어: Packet Collision Rate

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