[논문]주요 산림복원사업지 내 귀화식물의 특성과 공종 간 영향 관계

전용삼; 박준형; 권오일; 이혜정; 임채영

doi:10.13047/kjee.2022.36.5.481

주요 산림복원사업지 내 귀화식물의 특성과 공종 간 영향 관계
The Relationship between the Characteristics of Naturalized Plant and Working Type on Major Forest Restoration Sites 원문보기

한국환경생태학회지 = Korean journal of environment and ecology, v.36 no.5, 2022년, pp.481 - 495

전용삼 (한국산지보전협회 산림생태복원센터) , 박준형 (한국산지보전협회 산림생태복원센터) , 권오일 (한국산지보전협회 산림생태복원센터) , 이혜정 (한국수목원정원관리원 사회적가치성과실) , 임채영 (한국산지보전협회 산림생태복원센터)

초록
AI-Helper

이 연구는 산림복원사업 이후 유입되는 귀화식물과 생태계교란 식물의 실태 및 사업의 특성에 따라 나타나는 양상을 파악하는데 목적을 두고 있다. 현장조사는 산림청에서 수행한 산림복원사업지 29개소를 대상으로 2020년과 2021년 봄철(5~6월), 여름철(8~9월)로 나누어 연 2회 실시하였고, 사업 범위 밖의 지역은 조사에서 제외하여 실제 복원사업 후 도입 및 유입되었다고 볼 수 있는 식물을 파악할 수 있도록 하였다. 또한 대상지 내 분포하는 귀화식물상과 복원사업 준공내역 확인을 통해 현장에 실제 적용된 공종과의 연관성을 분석하였다. 전체 대상지에서 출현한 귀화식물은 29과 80속 108종 1아종으로 109분류군이며, 생태계교란 식물은 총 3과 7속 8종이 확인되었다. 귀화식물의 분류군 수와 귀화율은 사업 후 소요시간이 증가함에 따라 점차 감소하는 추세를 보였고, 귀화식물 분류군 수와 귀화율은 권역 간 유의적인 차이가 없는 것으로 나타났으나(p>0.05), 훼손 유형별 귀화식물 분류군 수의 경우 백두대간 단절 구간과 채석지, 시설부지 등의 유형에서 출현한 귀화식물 수가 상대적으로 많았다(p<0.05). 복원지 내 나지 및 비탈면의 녹화를 위한 식생도입 방법인 종자 파종, 나무 식재, 초본 식재, 떼붙임 공종의 유무에 따른 귀화율 비교 분석 결과, 종자파종을 할 경우 귀화율은 평균 15.545%로 파종 공종이 없는 경우의 평균 9.167%에 비해 높은 것으로 나타났고(p<0.05), 그 외 다른 식생도입 방법은 공종 적용 유무에 따라 귀화율의 유의적인 차이가 나타나지 않았다(p>0.05). 이는 식물체의 형태를 확인하고 어느 정도 제어할 수 있는 나무 식재와 초본 식재, 떼붙임 공종과는 달리 종자 상태에서 귀화식물 여부의 파악이 까다로운 종자 파종 공종이 산림복원사업지 내 귀화식물 도입에 큰 영향을 미치는 것을 의미한다. 따라서 복원지 내 종자 파종 시 종자 전문가에 의한 검수 과정의 도입이 필요할 것으로 사료된다. 이 연구의 결과는 향후 산림복원사업 시 식생 도입 및 사후관리의 방향설정에 도움이 되는 자료로 활용될 수 있을 것으로 판단된다.

Abstract ▼ AI-Helper

This study was designed to identify the actual state of naturalized plants and invasive alien species that cause disturbances to the ecosystem, plants which are introduced after forest restoration, and explore the implications resulting from the project. Onsite examination included 29 sites which have been subjected to forest restoration by the Korea Forest Service. Once these were chosen, activity took place twice a year in the spring (May-June) and in the summer (August-September) in 2020 and 2021. Areas not relevant to the project sites were excluded from this activity so that we could identify the plants that could be understood to have been introduced or brought into the site after the actual forest restoration. And the correlation was analyzed, between the naturalized flora within the project sites and the working types applied to the site through confirmation of completion of the restoration project. The naturalized plants appearing on the entire site cover a total of 109 taxa, which includes 29 families, 80 genera, 108 species and 1 subspecies, while invasive plants included 3 families, 7 genera and 8 species. The number of classifications and the naturalization rate gradually decreased over time, after the project. While there was no significant difference between the number of classification groups and the naturalization rate for naturalized plants between project sites, given the number of taxa of naturalized plants, organized by type of damage, there were relatively more naturalized plants that appeared in the severed section of the Baekdudaegan Mountain Range, as well as at quarry and facility sites. Seeding apparently results in naturalization rates as high as 15.545%, on average, based on comparisons of naturalization rates by sowing, seeding, planting, herb planting, and sod pitching channels, all of these being methods of vegetation for planting/greening of bareland and slopes within the project areas. With no seeding, it was 9.167%, higher than the average. As for other vegetation, there was no significant difference depending on application of the working type. This means that unlike the plants subjected to planting, the working type of seed planting which makes it difficult to identify whether a certain plant is a naturalized plant greatly affects the introduction of naturalized plants to the restoration sites, even when using herb planting and sod pitching to control plants and results. Therefore the study suggests that there be inspection by experts of seeds when sowing within restoration sites. The results of this study suggest good practices that will help to direct effective vegetation restoration and follow-up management.

주제어

표/그림 (15)

그림 Figure 1. The location map of survey site.
표 Table 1. The restoration characteristics of study sites
표 Table 1. (continued)
표 Table 2. The number of naturalized plant
표 Table 3. The number of naturalized plant by forest restoration site
표 Table 4. List of naturalized plant in forest restoration site
표 Table 4. (continued)
표 Table 4. (continued)
표 Table 5. The number of invasive alien plant by forest restoration site
표 Table 6. List of invasive alien plant in forest restoration site
그림 Figure 2. The inflow characteristic of naturalized plant by flow time(years) after forest restoration. (a) is the relation between the flow time and the number of taxa for naturalized plant. (b) is the relation between the flow time and naturalized ratio.
그림 Figure 3. The comparison of the no. taxa and naturalized ratio by the type and zone. The others are combined hiking trail with forest fire damage. (a) is comparison of no. taxa by zone. (b) is comparison of naturalized ratio by zone. (c) is comparison of no. taxa by type. (d) is comparison of naturalized ratio by type. Different letters in each column indicate significant differences according to Duncan's multiple range test(p<0.05). The vertical bars represent standard error of the means.
표 Table 7. The comparison result of naturalized ratio according to vegetation covering methods using t-test
표 Table 8. The result of phi coefficient analysis between major works and taxa of naturalized plant in forest restoration site(Top 30 species)
표 Table 8. (continued)

참고문헌 (27)

Cho, Y.H., J.H. Kim and S.H. Park(2016) Grasses and sedges in South Korea. Geobook, Seoul. (in Korean)
Choung, Y., B.M. Min, K.S. Lee, K.H. Cho, K.Y. Joo, J.O. Hyun, H.R. Na, H.K. Oh, G.H. Nam and J.S. Kim(2020) Wetland preference and life form of the vascular plants in the Korean peninsula. National Institute of Biological Resources, Incheon. (in Korean)
Jung, W.O.(2001) Effects of environmental factors on the stability and vegetation survival in cutting slope of forest roads. J. Korean Env. Res. & Reveg. Tech. 4(2): 74-83. (in Korean with English abstract)
Kang, H.M., S.H. Choi, D.H. Kim and J.T. Song(2017) A study on the restoration effects of vegetation restoration types. Korean J. Environ. Ecol. 31(2): 174-187. (in Korean with English abstract)
Kim, B.H., G.H. Kim, H.J. Kim and D.H. Kim(2000) Plant community survey and analysis for restoration of vegetation in coal-mined spoil lands-A case study of Hamtae coal-mined spoil lands in Taebaek city, Kangwondo-. J. Korean Env. Res. & Reveg. Tech. 3(4): 33-42. (in Korean with English abstract)
Kim, H.S. and J.G. Oh(2010) Distribution of naturalized plants in Dadohae national marine park. Korean J. Plant Res. 23(2): 187-196. (in Korean with English abstract)
Kim, J.D., J.W. Lee, B.J. Park, H.J. Lee, D.H. Lee, T.I. Heo, J.G. Byeon and J.H. Ahn(2020) Successional trends and vegetation types in the Baramjae area of Baekdudaegan. J. Korean Soc. For. Sci. 109(3): 249-258. (in Korean with English abstract)
Kim, J.S. and T.Y. Kim(2018) Woody plants of Korean peninsula. Dolbegae, Paju. (in Korean)
Kim, J.S., J.H. Kim and J.H. Kim(2018) Herbaceous plants of Korean peninsula: Plants living in seasides, rivers, wetlands and cities. Dolbegae, Paju. (in Korean)
Kim, K.H., H.C. Sung, J.Y. Choi and Y.J. Hur(2016) The revegetation using domestic plants. NEXUS Environmental Design Center, Gwacheon, 140pp. (in Korean)
Kim, N.C., H.Y. Kim and M.Y. Choi(2015) The study on the utilization of soil seed bank for the restoration of original vegetation. J. Korean Env. Res. Tech. 18(6): 201-214. (in Korean with English abstract)
Korea Forest Service(2015a) Illustrated grasses of Korea. Jinhan M&B, Seoul. (in Korean)
Korea Forest Service(2015b) Illustrated pteridophytes of Korea. Jinhan M&B, Seoul. (in Korean)
Korea Forest Service(2022) The process guide of forest restoration. Korea Forest Service, Daejeon, 212pp. (in Korean)
Korea National Arboretum(2017) Checklist of vascular plants in Korea. Korea National Arboretum, Pocheon. (in Korean)
Korea National Arboretum(2019) Checklist of alien plants in Korea. Korea National Arboretum, Pocheon. (in Korean)
Lee, C.S. and K. Lee(2015) Pteridophytes of Korea: Lycophytes & Ferns(2nd ed.). Geobook, Seoul. (in Korean)
Lee, M.J., H.K. Song, J.W. Lee and H.J. Kim(2003) Vegetation succession in the cut-slope of forest road-In case study on Chungcheong-do-. Jour. Korean For. Soc. 92(4): 397-408. (in Korean with English abstract)
Lee, S., J. Yun, D. Kang and J. Cha(2020) Planting status of ecological restoration project and improvement plan. J. Environ. Impact Assess. 29(5): 307-322. (in Korean with English abstract)
Lee, T.B.(2003) Coloured flora of Korea. Hyangmunsa, Seoul. (in Korean)
National Institute of Ecology(2021) Information for the field management of invasive alien species in Korea. National Institute of Ecology, Seocheon. (in Korean)
Oh, K.K. and S.G. Park(2003) Conservation status and restoration of evergreen broad-leaved forests in warm temperate region, Korea(II)-Restoration planning of vegetation in a case study areas-. Kor. J. Env. Eco. 17(1): 71-82. (in Korean with English abstract)
Society for Ecological Restoration International Science & Policy Working Group(2004) The SER international primer on ecological restoration. Society for Ecological Restoration International, Tucson. https://www.ser.org
Son, Y.H., C.D. Koo, C.S. Kim, P.S. Park, C.W. Yun and K.H. Lee(2016) Forest ecology. Hyangmunsa, Seoul, 346pp. (in Korean)
Yoon, J.W., H.T. Shin, M.H. Yi, G.S. Kim, J.W. Sung, K.H. Park, C.H. Lee and Y.S. Kim(2012) Status and management proposal of naturalized plant species within the cultural treasury area in Gyeongju national park, Korea. Kor. J. Env. Eco. 26(4): 550-558. (in Korean with English abstract)
You, J.H., K.H. Park and J.H. Choi(2014) Management plan and analysis of the characteristics of naturalized plants by ecological restoration of Gaeumjeong stream, Changwon-si. J. KILA 42(2): 48-59. (in Korean with English abstract)
You, J.H., Y.H. Kim, G. Chen, L.L. Zhang, S.B. Gwak, J.H. Jeong, Y.R. Seo, Y. Li and Z.L. Cui(2021) Vascular plants of Gyochon village in Gyeongju-si. Journal of the Korean Institute of Garden Design 7(1): 36-49. (in Korean with English abstract)

표제어: PCR

동의어: Packet Collision Rate

용어 설명 출처 목록 (6)

용어 설명: PCR은 세균 특이성이 있는 primer를 이용하여 적은 수의 세균이 있을지라도 쉽게 검출할 수 있는 유용한 방법이며, 이를 이용하여 구강 내 치면세균막이나 타액에서 직접 세균을 검출할 수 있게 되었다[8].

내보내기 구분	파일저장 인쇄 메일전송
구성항목	기본정보 상세정보 관리번호, 논문명, 저널/프로시딩명, 저자 , 발행년, 권, 호, 시작페이지, 끝페이지, 발행기관 관리번호, 논문명, 대등논문명, 저자 , 저널/프로시딩명, 발행기관, 발행년, 발행언어, 권, 호, 시작페이지, 끝페이지, ISBN, ISSN, 주제분야, 키워드, 초록(한글), 초록(영문), 저자(소속기관)
저장형식	Text(ASCII format) Excel format RefWorks Direct Export RIS format (for Reference Manager, ProCite, EndNote), Scholar's Aids, Mendeley
메일정보	받는사람 (필수) @ 보내는사람 (선택) @ 제목 내용 KISTI 검색결과 이메일 서비스
안내	총 건의 자료가 검색되었습니다. 다운받으실 자료의 인덱스를 입력하세요. (1-10,000) 검색결과의 순서대로 최대 10,000건 까지 다운로드가 가능합니다. 데이타가 많을 경우 속도가 느려질 수 있습니다.(최대 2~3분 소요) 다운로드 파일은 UTF-8 형태로 저장됩니다. 파일의 내용이 제대로 보이지 않을실 때는 웹브라우저 상단의 보기 -> 인코딩 -> 자동선택 여부를 확인하십시오. ~ Text(ASCII format) Excel format

연합인증