2022-25. 육상생태계 탄소저장흡수량 평가 체계구축

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(3) │참여연구진│ 본 『국립공원 육상생태계 탄소저장·흡수량 평가 체계구축』 사업은 다음과 같은 연구진에 의하여 수행되었습니다. 연 구 진 구. 분. 연구책임. 공동연구. 이. 름. 직. 위. 소. 속. 박홍철. 계 장. 국립공원연구원. 명현호. 기후변화연구센터장. 국립공원연구원. 조규남. 계 장. 국립공원연구원. 윤형진. 계 장. 국립공원연구원. 김진원. 책임연구원. 국립공원연구원. 박관수. 교 수. 충남대학교. 길승호. 교 수. 강원대학교. 이상진. 연구교수. 충남대학교. 김현숙. 연구교수. 충남대학교. 이상명. 연구원. 충남대학교. 이창규. 연구원. 충남대학교. 이창민. 연구원. 충남대학교. 김승원. 연구원. 충남대학교. 임재철. 연구원. 충남대학교. 이기배. 연구원. 충남대학교. 양승아. 연구원. 충남대학교. 정해중. 연구원. ㈜지오씨앤아이. 이종명. 연구원. ㈜지오씨앤아이. 민영기. 연구원. ㈜지오씨앤아이. 민병돈. 연구원. ㈜지오씨앤아이.

(4) 연 구 진 김석철. 연구원. ㈜지오씨앤아이. 김영빈. 연구원. ㈜지오씨앤아이. 곽광근. 연구원. ㈜지오씨앤아이. 박수진. 연구원. ㈜지오씨앤아이. 정준혁. 연구원. ㈜지오씨앤아이. 최창은. 연구원. 고려대학교. 심성기. 연구원. ㈜솔브케이. 정순영. 대 표. ㈜서로. 이윤경. 연구원. ㈜포레스트아이디. 조동현. 연구원. ㈜포레스트아이디. 현진오. 소 장. 동북아생물다양성연구소. 노남진. 교 수. 강원대학교. 공동연구. 자문위원. 연 구 지 원 이 름. 직. 정용상. 원 장. 국립공원연구원. 채희영. 정책개발실장. 국립공원연구원. 박종길. 부 장. 국립공원공단 자원보전처. 강호남. 부 장. 국립공원공단 자원보전처. 박은희. 차 장. 국립공원공단 자원보전처. 나경태. 차 장. 국립공원공단 자원보전처. 이나연. 담당관. 국립공원공단 탄소중립전략실. II │국립공원공단│국립공원연구원│. 위. 소 속.

(5) │목차│ Ⅰ. 추진개요 ····································································································3 1. 배경 및 목적 ································································································· 3 가. 배경 및 필요성 ·································································································· 3 나. 목적 ··················································································································· 4. 2. 추진범위 ········································································································ 5 가. 공간범위 ············································································································ 5 나. 시간범위 ············································································································ 5 다. 내용범위 ············································································································ 5. Ⅱ. 추진방법 ····································································································9 1. 고정조사구 체계구축 ····················································································· 9 2. 식물생태정보 분석 ······················································································ 10 가. 종수-면적 곡선 작성 ······················································································· 10 나. 상대우점치 분석 ······························································································ 10 다. 종다양성지수 분석 ··························································································· 11 라. 식물군락분류 ··································································································· 11 마. Ordination 분석 ····························································································· 11. 3. 토양탄소배출량 조사 ··················································································· 12 가. 대상지 현황 ····································································································· 12 나. 배출량 측정방법 ······························································································ 13. │국립공원 육상탄소흡수원 구축사업 효과성 모니터링 체계구축│ I.

(6) │목차│ Ⅲ. 추진결과 ··································································································17 1. 고정조사구 체계구축 ··················································································· 17 2. 식물생태정보 분석결과 ················································································ 39 가. 조사구 개수(면적) 설계 적정성 검토결과 ························································ 39 나. 조사구-출현종 행렬분석 결과 ········································································· 40 다. 상대우점치 분석결과 ······················································································· 41 라. 종다양성지수 분석결과 ···················································································· 41 마. 식물군락분류 결과 ··························································································· 42 바. 조사구별 식생특성에 따른 서열분석 결과 ······················································· 43 사. 탄소저장량과 종다양도 관계성 분석결과 ························································· 45. 3. 토양탄소배출량 조사결과 ············································································ 46. Ⅳ. 부록 ·········································································································53. II │국립공원공단│국립공원연구원│.

(7) │표목차│ [표 1-1] 국립공원 육상생태계 탄소저장량 평가 결과 ··················································································4 [표 2-1] 소백산국립공원 토양미생물 호흡량 조사구 현황 ·········································································12 [표 3-1] 공원별 고정조사구 구축 현황 ·······································································································17 [표 3-2] 지리산국립공원 탄소흡수원 유형별 조사구 현황 ·········································································18 [표 3-3] 한려해상국립공원 탄소흡수원 유형별 조사구 현황 ······································································19 [표 3-4] 경주국립공원 탄소흡수원 유형별 조사구 현황 ·············································································20 [표 3-5] 계룡산국립공원 탄소흡수원 유형별 조사구 현황 ·········································································21 [표 3-6] 설악산국립공원 탄소흡수원 유형별 조사구 현황 ·········································································22 [표 3-7] 속리산국립공원 탄소흡수원 유형별 조사구 현황 ·········································································23 [표 3-8] 내장산국립공원 탄소흡수원 유형별 조사구 현황 ·········································································24 [표 3-9] 가야산국립공원 탄소흡수원 유형별 조사구 현황 ·········································································25 [표 3-10] 덕유산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································26 [표 3-11] 오대산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································27 [표 3-12] 주왕산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································28 [표 3-13] 태안해안국립공원 탄소흡수원 유형별 조사구 현황 ···································································29 [표 3-14] 다도해해상국립공원 탄소흡수원 유형별 조사구 현황 ································································30 [표 3-15] 북한산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································31 [표 3-16] 치악산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································32 [표 3-17] 월악산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································33 [표 3-18] 소백산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································34 [표 3-19] 변산반도국립공원 탄소흡수원 유형별 조사구 현황 ···································································35 [표 3-20] 월출산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································36 [표 3-21] 무등산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································37 [표 3-22] 태백산국립공원 탄소흡수원 유형별 조사구 현황 ·······································································38. │국립공원 육상탄소흡수원 구축사업 효과성 모니터링 체계구축│ III.

(8) │그림목차│ [그림 2-1] 고정조사구 설치 모습 ··················································································································9 [그림 2-2] 소백산국립공원 토양미생물 호흡량 조사구 위치 ······································································12 [그림 2-3] 토양탄소배출량 측정을 위한 조사구 설치과정 ·········································································13 [그림 2-4] 휴대용 CO2 가스 분석기(EGM-5)와 SRC-2 토양 호흡 챔버 ··············································14 [그림 3-1] 지리산국립공원 탄소흡수원 유형별 조사구 위치 ······································································18 [그림 3-2] 한려해상국립공원 탄소흡수원 유형별 조사구 위치 ··································································19 [그림 3-3] 경주국립공원 탄소흡수원 유형별 조사구 위치 ·········································································20 [그림 3-4] 계룡산국립공원 탄소흡수원 유형별 조사구 위치 ······································································21 [그림 3-5] 설악산국립공원 탄소흡수원 유형별 조사구 위치 ······································································22 [그림 3-6] 속리산국립공원 탄소흡수원 유형별 조사구 위치 ······································································23 [그림 3-7] 내장산국립공원 탄소흡수원 유형별 조사구 위치 ······································································24 [그림 3-8] 가야산국립공원 탄소흡수원 유형별 조사구 위치 ······································································25 [그림 3-9] 덕유산국립공원 탄소흡수원 유형별 조사구 위치 ······································································26 [그림 3-10] 오대산국립공원 탄소흡수원 유형별 조사구 위치 ···································································27 [그림 3-11] 주왕산국립공원 탄소흡수원 유형별 조사구 위치 ···································································28 [그림 3-12] 태안해안국립공원 탄소흡수원 유형별 조사구 위치 ································································29 [그림 3-13] 다도해해상국립공원 탄소흡수원 유형별 조사구 위치 ····························································30 [그림 3-14] 북한산국립공원 탄소흡수원 유형별 조사구 위치 ···································································31 [그림 3-15] 치악산국립공원 탄소흡수원 유형별 조사구 위치 ···································································32 [그림 3-16] 월악산국립공원 탄소흡수원 유형별 조사구 위치 ···································································33 [그림 3-17] 소백산국립공원 탄소흡수원 유형별 조사구 위치 ···································································34 [그림 3-18] 변산반도국립공원 탄소흡수원 유형별 조사구 위치 ································································35 [그림 3-19] 월출산국립공원 탄소흡수원 유형별 조사구 위치 ···································································36 [그림 3-20] 무등산국립공원 탄소흡수원 유형별 조사구 위치 ···································································37 [그림 3-21] 태백산국립공원 탄소흡수원 유형별 조사구 위치 ···································································38 [그림 3-22] 조사구 개수와 출현종수 간 그래프 ························································································39 [그림 3-23] 조사구-출현종 행렬분석 결과 ·································································································40 [그림 3-24] TWINSPAN 식물군락분류 결과 ·····························································································42 [그림 3-25] DCA Ordination 분석에 따른 군락별 분포현황 ··································································43 [그림 3-26] 조사구별 생태환경특성에 따른 DCA Ordination 분석 결과 ···············································44 [그림 3-27] 토양권 및 식생권 탄소저장량과 종다양도 관계 그래프 ························································45. IV │국립공원공단│국립공원연구원│.

(9) │그림목차│ [그림 3-28] 소백산국립공원 탄소흡수원 유형별 연간 토양탄소배출량 ·····················································46 [그림 3-29] 소백산국립공원 탄소흡수원 유형에 따른 계절별 연간 토양탄소배출량 ································48 [그림 3-30] 소백산국립공원 계절에 따른 탄소흡수원 유형별 연간 토양탄소배출량 ································48 [그림 3-31] 침엽수군락 및 활엽수군락의 토양온도-토양탄소배출량 관계 그래프 ···································49 [그림 3-32] 아고산대 침엽수군락 및 아고산대 초지의 토양온도-토양탄소배출량 관계 그래프 ··············50 [그림 3-33] 인공림의 토양온도-토양탄소배출량 관계 그래프 ···································································50. │국립공원 육상탄소흡수원 구축사업 효과성 모니터링 체계구축│ V.

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(11) Ⅰ. 추진개요.

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(13) Ⅰ. 추진개요 1. 배경 및 목적. Ⅰ. 추진개요 1. 배경 및 목적. 가. 배경 및 필요성 2050 탄소중립(carbon neutral)의 글로벌 의제화 2016년 발효한 파리협정 및 2019년 UN기후정상회의 이후 전 세계는 기후위기 해결을 위한 글로벌 의제로서, 2050년까지 전 세계 탄소중립 실현을 목표로 하고 있음 대한민국 국가온실가스감축목표(National Determined Contribution, NDC) 상향 조정 제26차 유엔기후변화협약 당사국총회(`21.10.)에서 우리나라는 국가온실가스감축목표(NDC)를 2030년까지 2018년 온실가스 배출량 대비 26.3% 감축한다는 기존 목표에서 23.7% 상향조정한 40.0%로 목표를 수정하였음 자연기반해법(Nature-based Solutions, NbS) 강화 자연기반해법은 자연·생태계 본연의 회복력에 기반하여 기후변화 문제를 해결하고자 하는 접근방식으로 , 자연·생태계의 탄소흡수원 기능을 유지, 보전 그리고 향상시킴으로써 기후변화에 대응할 수 있다는 새로운 해법으로 제시되고 있음 자연기반해법은 특히 국립공원과 같은 보호지역 자연·생태계의 탄소저장·흡수 기능에 주목 하고 있으며, 보호지역의 확대 및 정책개선, 재원 증대 자체가 결과적으로 기후변화 완화와 적응 기능을 강화할 것이라는 점을 강조하고 있음. │국립공원 육상생태계 탄소저장·흡수량 평가 체계구축│ 3.

(14) 국립공원 탄소저장량, 우리나라 산림의 탄소저장량(약 3,250백만 CO2톤)의 약 11% 차지 22개 전 공원 육상생태계 탄소저장량 약 3억4천7백만 CO2톤1) 단위면적당 탄소저장량 비교시 우리나라 산림 평균의 1.7배*, 아시아 산림 평균의 1.8배**, 세계 산림 평균의 1.5배*** 많음 * 542 CO2톤/ha, ** 499 CO2톤/ha, *** 598 CO2톤/ha [표 1-1] 국립공원 육상생태계 탄소저장량 평가 결과 합 계. 구분. 총 량. 면적(ha). 385,650. 저장량(CO2톤). 347백만. 식생권 (초지, 습지 제외) 총 량. ha 당. 토양권 (초지, 습지 포함) 총 량. 382,830 219백만. ha 당 385,650. 570.8. 128백만. 332.2. 국립공원 탄소중립 대응을 위한 공원별 육상탄소저장·흡수량 중장기 평가체계 필요 탄소흡수원 유형별 식생권 탄소흡수량 변화 모니터링 체계 구축 요구도 증대 토양권 미생물 호흡에 따른 탄소배출량 정량평가 및 중장기 모니터링 필요성 증가 고정조사구 구축·조사를 통한 국립공원 육상생태계 탄소흡수량 중장기 평가 프로토콜 필요. 나. 목적 국립공원 육상생태계 탄소흡수원 유형별 탄소저장·흡수량 평가를 위한 중장기 프로토콜 구축. 1) 국립공원연구원(2021) 국립공원 생태계부문 탄소저장량 평가 보고서. 4 │국립공원공단│국립공원연구원│.

(15) Ⅰ. 추진개요 2. 추진범위. 2. 추진범위. 가. 공간범위 2021년 국립공원연구원에서 수행한 「국립공원 육상생태계 탄소저장량 평가」 사업의 조사지역(22개 공원 222개소) 중 산지습지, 초지를 제외한 산림지역. 나. 시간범위 2022년 4월부터 2022년 12월까지 (단, 현장조사는 2022년 11월까지 수행). 다. 내용범위 식생권 탄소저장·흡수량 중장기 조사·모니터링 체계구축 (고정조사구 상세구축) 21개 공원(212개소) 고정조사구 현장체계구축 ※ 한라산국립공원(10개소) 제외: 대다수 조사구가 천연보호구역 내 위치하여 행위제한 (생태환경정보 수집) 조사구별 식생구조 및 종조성 등 생태학적 연계 분석(전 공원 대상) 토양권 미생물호흡에 따른 토양탄소배출량 평가 (시범조사) 소백산국립공원 대상 주요 탄소흡수원 유형별 토양탄소배출량 측정·조사 * 국립공원 중 단위면적당 탄소저장량이 가장 높은 공원으로 시범대상지 선정(한라산 제외) 이동식 토양탄소배출량 측정기를 활용한, 계절별 토양탄소배출량 실측 데이터 수집. │국립공원 육상생태계 탄소저장·흡수량 평가 체계구축│ 5.

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(17) Ⅱ. 추진방법.

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(19) Ⅱ. 추진방법 1. 고정조사구 체계구축. Ⅱ. 추진방법 1. 고정조사구 체계구축. 우리나라 전체 22개 국립공원 중 한라산국립공원을 제외한 21개 국립공원 내 각 고정 조사구에서 30m×30m 고정조사구 설치. 한라산국립공원은 대다수 조사구 위치가 천연 보호구역에 위치하고 있어 훼손방지를 목적으로 별도의 고정조사구 미설치 각 조사구는 2021년 국립공원 육상생태계 탄소저장량 평가 조사구와 동일한 공간으로 위치시키되, 동일한 임분 유형으로 정방형의 고정조사구 설치가 불가능한 경우에는 20m×45m 또는 60m×15m 등 조사구 면적이 900㎡가 될 수 있도록 고정형 조사구 설치 줄자, 로프, 지주팩을 이용하여 지표면에 고정조사구 경계를 확인할 수 있도록 하였으며, 고정조사구의 크기 및 시작점의 식별이 용이하도록 조사구 각 모서리에는 알루미늄 지주대 (1m)를 설치하고 상부에 눈에 띄는 색상의 리본 부착. [그림 2-1] 고정조사구 설치 모습. │국립공원 육상생태계 탄소저장·흡수량 평가 체계구축│ 9.

(20) 2. 식물생태정보 분석. 가. 종수-면적 곡선 작성 조사구의 총 면적 및 조사구 수 설계에 대한 적절성을 검토하기 위해, Jackknife 방법2)에 따라 출현종수와 조사구 총 면적 간 그래프를 작성함. 나. 상대우점치 분석 조사구내 층위별 각 수종의 상대적 우세도를 비교하기 위해 Curtis and McIntosh (1951)3)의 중요도를 백분율로 표현한 상대우점치(IP, Importance Percentage)를 분석함. 단, 습지 및 초지 조사구는 제외하였으며, 초본층 및 관목층을 제외한 흉고직경 6cm 이상 목본식물을 대상으로 함 어느 한 수종의 밀도 ‣ 상대밀도     ×  전체 수종의 밀도 어느 한 수종의 피도 ‣ 상대피도     ×  전체 수종의 피도 ‣ 상대우점치   . 상대밀도  상대피도  . 층위별 가중치를 부여하고 군락 내 모든 종의 우세도를 비교하기 위해 평균상대우점치 (MIP, Mean Importance Percentage)를 분석하였음. 단 , 습지 및 초지 조사구는 제외하였으며, 초본층 및 관목층을 제외한 흉고직경 6cm 이상 목본식물을 대상으로 함 ‣ 평균상대우점도   . 상층  ×   중층  ×   하층  ×   . 2) Palmer, M.W. (1991) Estimating species richness: the second order jackknife reconsidered. Ecology 72: 1512-1513. 3) Curtis, J.T. and R.P. McIntosh (1951) An upland forest continuum in the prairie-forest border region of Wisconsin. Ecology 32: 476-496.. 10 │국립공원공단│국립공원연구원│.

(21) Ⅱ. 추진방법 2. 조사구별 식물생태정보 분석. 다. 종다양성지수 분석 조사구 내 종 구성 상태의 다양한 정도를 확인하기 위해 Shannon의 수식4)을 적용하여, 종 다양도, 최대 종 다양도, 균제도, 우점도를 분석하였음. 단, 습지 및 초지 조사구는 제외하였으며, 초본층 및 관목층을 제외한 흉고직경 6cm 이상 목본식물을 대상으로 함 ‣ 종다양도  ′   .    × log  . ‣ 최대종다양도  ′ max  log . ′ ‣ 균재도  ′     ′max ‣ 우점도       ′ 단   어느 한 종의 개체수   전체종의 개체수   종수 . 라. 식물군락분류 조사구별 식생조사 자료를 바탕으로 군락별 식물사회학적 특성을 파악하기 위해 TWINSPAN에 의한 군락분류를 실시하였음. 초본층을 제외한 목본식물을 대상으로 각 조사구별 종구성과 종별 평균상대우점치 값을 기준으로 실시하였으며, PC-ORD6 소프트웨어를 사용함. 마. Ordination 분석 군락분류를 통해 그룹화된 군락의 분포특성을 파악하기 위해 DCA ordination5) 분석을 실시함. 초본층을 제외한 목본식물을 대상으로 각 조사구별 평균상대우점치와 입지환경 자료를 바탕으로 실시하였으며, PC-ORD6 소프트웨어를 사용함 4) Shannon, C.E. and W. Weaver (1963) The mathematical theory of communication. University of Illinois Press, Urbana, 117pp.; Pielou, E.C. (1975) Mathematical ecology. John Wiley & Sons, N.Y., 385pp. 5) Hill, M.O. (1979) DECORANA - a FORTRAN Program for Detrended Correspondence Analysis and Reciprocal Averaging. Ecology and Systematics, Cornel Univ., Ithaca, New York, 52pp.. │국립공원 육상생태계 탄소저장·흡수량 평가 체계구축│ 11.

(22) 3. 토양탄소배출량 조사. 가. 대상지 현황 토양미생물 호흡에 따른 토양탄소배출량 조사는 소백산국립공원을 대상으로 시범조사 탄소흡수원 유형에 따라 기 구축된 고정조사구를 중심으로 활엽수군락 3개소, 침엽수 군락 3개소, 인공조림지 3개소, 아고산대 상록침엽수군락 1개소, 아고산대 초지(비로봉) 1개소로 구분하여 총 11개의 조사구에서 측정 ·조사됨 [표 2-1] 소백산국립공원 토양미생물 호흡량 조사구 현황 유형. 활엽수군락. 침엽수군락. 인공조림지. 아고산대 침엽수군락. 아고산대 초지. 합 계. 조사구수. 3. 3. 3. 1. 1. 11. [그림 2-2] 소백산국립공원 토양미생물 호흡량 조사구 위치. 12 │국립공원공단│국립공원연구원│.

(23) Ⅱ. 추진방법 3. 토양탄소배출량 조사. 나. 배출량 측정방법 조사구 설치 토양미생물호흡에 따른 토양탄소배출량 측정을 위해 소백산국립공원 각 조사구 내에 1m×1m의 조사구를 설치하고 조사구 내 지피식생을 모두 제거함 조사구 경계선 밖으로 폭 약 25㎝, 깊이 약 70㎝의 내외의 도랑을 파내어 경계면의 모든 식물뿌리를 끊고 방근매트를 도랑 주위로 둘러 식물뿌리가 침입하지 못하도록 함 토양탄소배출량 조사 시 조사구 내 이입된 식물이 존재할 경우 목본류는 지상부를 절단 하고, 초본류는 토양이 교란되지 않도록 주의하며 이입된 식물 제거 휴대용 이산화탄소 가스분석기 활용하였으며, 매 측정 시 토양 표층의 교란을 최소화하기 위하여 칼라(collar)를 높이 8㎝로 제작하여 방형구 중앙에 설치. <조사구 주변 도랑 파기>. <조사구 방근매트 설치>. [그림 2-3] 토양탄소배출량 측정을 위한 조사구 설치과정. 측정 장비 휴대용 이산화탄소 가스분석기는 EGM-5(PP Systems)를 사용하였으며, SRC-2 토양 호흡챔버를 연결하여 Dynamic closed chamber method를 이용해 측정. │국립공원 육상생태계 탄소저장·흡수량 평가 체계구축│ 13.

(24) 토양호흡측정챔버(SRC-2, Soil Respiration Chamber)는 Soil CO2 efflux를 측정 하는데 사용되며, 호흡속도(g m-2 hr-1)는 일정기간 동안 챔버 CO2 농도의 변화속도를 측정하여 계산됨. <EGM-5>. <SRC-2>. [그림 2-4] 휴대용 CO2 가스 분석기(EGM-5)와 SRC-2 토양 호흡 챔버. 측정 방법 측정시기는 한정된 사업수행기간에 따라 5월(봄철), 7월(여름철), 9월(가을철 ), 11월 (겨울철) 계절별로 1일 동안 2시간 간격으로 12회 측정 단, 사업수행기간의 한계에 따라 겨울철 토양탄소배출량 측정에 제한이 있어, 이른 봄이나 늦가을의 CO2 발생량을 동절기의 방출량과 동일하게 취급하는 간접측정법을 활용함 즉, 본 사업에서 연간 토양탄소배출량을 산출함에 있어서 12월부터 2월까지의 이산화탄소 발생량이 늦가을인 11월에 조사된 발생량과 동일하다는 가정 하에 연간 토양탄소배출량을 추정하였음 봄철인 3월에서 5월까지의 토양탄소배출량은 5월에 조사된 자료를 이용하였으며, 여름철인 6월에서 8월의 토양탄소배출량은 7월에 조사된 자료 적용. 가을철인 9월에 조사된 자료는 10월에 동일하게 적용하여 연간 토양탄소배출량 산출. 14 │국립공원공단│국립공원연구원│.

(25) Ⅱ. 추진방법 3. 토양탄소배출량 조사. Ⅲ. 추진결과. │국립공원 육상생태계 탄소저장·흡수량 평가 체계구축│ 15.

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(27) Ⅲ. 추진결과 1. 고정조사구 체계구축. Ⅲ. 추진결과 1. 고정조사구 체계구축. 고정조사구 총괄현황 [표 3-1] 공원별 고정조사구 구축 현황 공원명. 활엽수 군락. 침엽수 군락. 침활횬효 군락. 인공 조림지. 아고산대 침엽수군락. 산지습지. 초지. 조사구수. 합 계. 116. 48. 25. 6. 9. 6. 2. 212. 지리산. 4. 2. 1. 1. 1. 1. -. 10. 한려해상. 3. 2. 1. -. -. -. -. 6. 경주. 6. 2. 1. -. -. 1. -. 10. 계룡산. 8. 2. 2. -. -. -. -. 12. 설악산. 6. 2. 1. -. 1. -. -. 10. 속리산. 6. 3. 1. -. -. -. -. 10. 내장산. 9. 2. 1. -. -. 1. -. 13. 가야산. 6. 2. 1. -. -. 1. -. 10. 덕유산. 6. 2. 1. -. 1. -. -. 10. 오대산. 10. 4. 4. -. 4. 1. 1. 24. 주왕산. 6. 3. 1. -. -. -. -. 10. 태안해안. 2. 3. 1. -. -. -. -. 6. 다도해해상. 2. 2. 1. -. -. -. -. 5. 북한산. 6. 3. 1. -. -. -. -. 10. 치악산. 6. 2. 1. 1. -. -. -. 10. 월악산. 6. 2. 1. 1. -. -. -. 10. 소백산. 4. 2. 1. 1. 1. -. 1. 10. 변산반도. 4. 1. 1. -. -. -. -. 6. 월출산. 6. 3. 1. -. -. -. -. 10. 무등산. 6. 2. 1. -. -. 1. -. 10. 태백산. 4. 2. 1. 2. 1. -. -. 10. │국립공원 육상생태계 탄소저장·흡수량 평가 체계구축│ 17.