5 research outputs found

    Impact of Deforestation on Agro-Environmental Variables in Cropland, North Korea

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    Deforestation in North Korea is becoming the epitome of the environmental change occurring in the Korean Peninsula. This study estimates the agro-environmental variables of North Korea’s croplands and analyzes the impact of deforestation using the GEPIC (GIS-based EPIC (Environmental Policy Integrated Climate)) model and time-series land cover maps. To identify the changes in agricultural quality under deforestation, wind erosion, water erosion, organic carbon loss, and runoff were selected as the agro-environmental variables having an impact on cropland stability and productivity. Land cover maps spanning the past three decades showed that 75% of the forests were converted to croplands and that 69% of all converted croplands were originally forests, confirming the significant correlation between deforestation and cropland expansion in North Korea. Despite limitations in the verification data, we conducted qualitative and quantitative validation of the estimated variables and confirmed that our results were reasonable. Over the past 30 years, agro-environmental variables showed no clear time-series changes resulting from climate change, but changes due to spatial differences were seen. Negative changes in organic carbon loss, water erosion, and runoff were observed, regardless of the crop type. On newly-converted agricultural lands, runoff is 1.5 times higher and water-driven erosion and soil organic loss are more than twice as high compared to older croplands. The results showed that the agro-environment affected by deforestation had an impact on cropland stability and productivity

    μ ‘κ·ΌλΆˆκ°€μ§€μ—­μΈ λΆν•œμ˜ μ‹œκ³„μ—΄ 토지피볡도 맀핑 및 μ‚°λ¦Ό λ³€ν™” 동ν–₯ 뢄석

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    ν•™μœ„λ…Όλ¬Έ(석사) -- μ„œμšΈλŒ€ν•™κ΅λŒ€ν•™μ› : 농업생λͺ…κ³Όν•™λŒ€ν•™ μƒνƒœμ‘°κ²½Β·μ§€μ—­μ‹œμŠ€ν…œκ³΅ν•™λΆ€(μƒνƒœμ‘°κ²½ν•™), 2021.8. 이동근.North Korea, as an inaccessible area, has little research on land cover change, but it is very important to understand the changing trend of LULCC and provide information previously unknown to North Korea. This study therefore aimed to construct and analyze a 30-m resolution modern time-series land use land cover (LULC) map to identify the LULCCs over long time periods across North Korea and understand the forest change trends. A land use and land cover (LULC) map of North Korea from 2001 to 2018 was constructed herein using semi-permanent point classification and machine learning techniques on satellite image time-series data. The resultant relationship between cropland and forest cover, and the LULC changes were examined. The classification results show the effectiveness of the methods used in classifying the time series of Landsat images for LULC, wherein the overall accuracy of the LULC classification results was 97.5% Β± 0.9%, and the Kappa coefficient was 0.94 Β± 0.02. Using LULC change detection, our research effectively explains the change trajectory of North Korea’s current LULC, providing new insights into the change characteristics of North Korea’s croplands and forests. Further, our results show that North Korea’s urban area has increased significantly, its forest cover has increased slightly, and its cropland cover has decreased. We determined that North Korea’s Forest protection policies have led to the forest restoration. Thus, as agriculture is one of North Korea’s main economic contributors, croplands have been forced to relocate, expanding to other regions to compensate for the land loss caused by forest restoration.λΆν•œμ€ μ„Έκ³„μ—μ„œ κ°€μž₯ μ‹¬κ°ν•˜κ²Œ ν™©νν™”λœ μ‚°λ¦Ό 쀑 ν•˜λ‚˜λ₯Ό ν¬ν•¨ν•˜κ³  μžˆμ§€λ§Œ μ΅œκ·Όμ—λŠ” μ‚°λ¦Ό 볡원을 κ°•μ‘°ν•˜κ³  μžˆλ‹€. μ‚°λ¦Ό 볡원이 μΌμ–΄λ‚˜λŠ” 정도λ₯Ό μ΄ν•΄ν•˜κΈ° μœ„ν•΄μ„œλŠ” 토지 이용과 토지 피볡 λ³€ν™” κ²½ν–₯ (LULCC)을 이해해야 ν•œλ‹€. λ”°λΌμ„œ λ³Έ μ—°κ΅¬λŠ” 30m ν•΄μƒλ„μ˜ ν˜„λŒ€ μ‹œκ³„μ—΄ 토지 이용 토지 피볡 (LULC)지도λ₯Ό ꡬ성 및 λΆ„μ„ν•˜μ—¬ λΆν•œ μ „μ—­μ˜ μž₯κΈ° LULCCλ₯Ό μ‹λ³„ν•˜κ³  μ‚°λ¦Ό λ³€ν™” μΆ”μ„Έλ₯Ό μ΄ν•΄ν•˜λŠ” 것을 λͺ©ν‘œλ‘œ ν•œλ‹€. 2001 - 2018 λ…„ κΈ°κ°„ λ™μ•ˆ κ΅­κ°€μ˜ LULCμ§€λ„λŠ” 30m 해상도 μœ„μ„± 이미지 μ‹œκ³„μ—΄ 데이터λ₯Ό 기반으둜 반영ꡬ적 포인트 λΆ„λ₯˜ 및 기계 ν•™μŠ΅μ„ μ‚¬μš©ν•˜μ—¬ κ΅¬μ„±λ˜μ—ˆμœΌλ©°, μ΄λŠ” GEE (Google Earth Engine)μ—μ„œ μˆ˜μ§‘ ν•œ ν˜„μƒ 학적 정보와 ν•¨κ»˜ μ‚¬μš©λ˜κ³  μžˆλ‹€. λ˜ν•œ LULCC 탐지기 법과 κ²½μž‘μ§€ 변화와 κ³ λ„μ˜ 관계λ₯Ό κ³ λ €ν•˜μ—¬ 2001 - 2018 λ…„ λΆν•œμ˜ μ‚°λ¦Ό λ³€ν™”λ₯Ό ν‰κ°€ν•˜μ˜€λ‹€. LULC 맡 결과의 전체 λΆ„λ₯˜ μ •ν™•λ„λŠ” 97.5 % Β± 0.9 %이고, Kappa κ³„μˆ˜λŠ” 0.94 Β± 0.02 이닀. LULCC νƒμ§€λŠ” λ˜ν•œ 2001 - 2018 년에 λΆν•œμ˜ μ‚°λ¦Ό 면적이 μ•½κ°„ μ¦κ°€ν•œ κ²ƒμœΌλ‘œ λ‚˜νƒ€λ‚¬λ‹€. 일반적으둜 μ‚°λ¦Ό 피볡 면적은 크게 λ³€ν•˜μ§€ μ•Šμ•˜μœΌλ‚˜ 남뢀와 쀑뢀 μ§€μ—­μ˜ μ‚°λ¦Ό 볡원과 뢁뢀와 μ„œλΆ€μ˜ κ²½μž‘μ§€ μƒλŒ€μ  증가 μΈ‘λ©΄μ—μ„œ λšœλ ·ν•œ 곡간적 λ³€ν™”κ°€ κ΄€μ°°λ˜μ—ˆλ‹€. λΆν•œμ˜ νŠΉμ„±κ³Ό μ‚°λ¦Ό μ •μ±… λ¬Έμ„œλ₯Ό κ²€ν†  ν•œ κ²°κ³Ό λΆν•œ κ·ΌλŒ€ μ‚°λ¦Όμ˜ 일뢀 지역이 λ³΅μ›λ˜κ³  μžˆμŒμ„ ν™•μΈν•˜μ˜€λ‹€.Chapter 1. Introduction 1 Chapter 2. Study Area 7 Chapter 3. Materials and Methods 8 3.1. Study overview 8 3.2. Data Collection 9 3.3. Data Processing 11 3.4. Classification Process 12 3.5. LULCC Analysis 14 3.6. Reference Data Collection and Classification Accuracy Validation 15 Chapter 4. Results 17 4.1. LULC Classification Accuracy Assessment 17 4.2. LULC Classification Results 20 4.3. LULC Change Detection 22 4.4. Relation with mountainous cropland and elevation 26 Chapter 5. Discussion 28 5.1. Interpretation and explanation of the forest change in North Korea 28 5.2. Importance of spatial analysis and future research directions 30 5.3. Limits and Advantages 32 Chapter 6. Conclusion 34 Bibliography 36 Appendix 44 Abstract in Korean 51석

    Assessment of Agricultural Drought Considering the Hydrological Cycle and Crop Phenology in the Korean Peninsula

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    Hydrological changes attributable to global warming increase the severity and frequency of droughts, which in turn affect agriculture. Hence, we proposed the Standardized Agricultural Drought Index (SADI), which is a new drought index specialized for agriculture and crops, and evaluated current and expected droughts in the Korean Peninsula. The SADI applies crop phenology to the hydrological cycle, which is a basic element that assesses drought. The SADI of rice and maize was calculated using representative hydrological variables (precipitation, evapotranspiration, and runoff) of the crop growing season. In order to evaluate the effectiveness of SADI, the three-month Standardized Precipitation Index, which is a representative drought index, and rainfed crop yield were estimated together. The performance evaluation of SADI showed that the correlation between rainfed crop yield and SADI was very high compared with that of existing drought index. The results of the assessment of drought over the past three decades provided a good indication of a major drought period and differentiated the results for crops and regions. The results of two future scenarios showed common drought risks in the western plains of North Korea. Successfully validated SADIs could be effectively applied to agricultural drought assessments in light of future climate change, and would be a good example of the water-food nexus approach

    Google Earth Engine을 μ΄μš©ν•œ λΆν•œμ˜ μ‚°λ¦Ό 황폐화 연ꡬ

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    ν•™μœ„λ…Όλ¬Έ(석사) -- μ„œμšΈλŒ€ν•™κ΅λŒ€ν•™μ› : 농업생λͺ…κ³Όν•™λŒ€ν•™ μƒνƒœμ‘°κ²½Β·μ§€μ—­μ‹œμŠ€ν…œκ³΅ν•™λΆ€(μƒνƒœμ‘°κ²½ν•™), 2021.8. 이동근.μ‚°λ¦Ό ν™©νν™”λŠ” μ‚°λ¦Ό μƒνƒœκ³„λ₯Ό νŒŒκ΄΄ν•˜λ©° λ¬Ό μ €μž₯ 및 곡급과 λŒ€κΈ°μ˜€μ—Όμ„ μ€„μ΄λŠ” λ“± 산림이 가지고 μžˆλŠ” κΈ°λŠ₯을 μ €ν•˜μ‹œν‚¨λ‹€. ν™©νν™”λ‘œ μΈν•œ μ‚°λ¦Όμ˜ κΈ°λŠ₯ μ €ν•˜λŠ” κΈ°ν›„λ³€ν™” λŒ€μ‘ 및 λŒ€κΈ°μ§ˆ μΈ‘λ©΄μ—μ„œ 뢀정적인 영ν–₯을 미치게 λœλ‹€. λΆν•œμ€ 세계 3개 μ‚°λ¦Ό ν™©νμ§€μ—­μœΌλ‘œ 1990λ…„λŒ€λΆ€ν„° μ΅œκ·ΌκΉŒμ§€ μ‚°λ¦Όμ˜ μ•½ 28%κ°€ ν™©νν™”λ˜μ—ˆλ‹€λŠ” ꡭ립 μ‚°λ¦Ό κ³Όν•™μ›μ˜ 연ꡬ결과가 μžˆλ‹€. ν•˜μ§€λ§Œ 곡인된 ν†΅κ³„λŠ” μ—†μ–΄ μΆ”ν›„ 볡원을 μœ„ν•΄μ„œλŠ” μ •ν™•ν•œ ν˜„ν™© νŒŒμ•…μ΄ ν•„μš”ν•œ 싀정이닀. 일반적인 μ‚°λ¦Ό ν™©νν™”μ™€λŠ” 달리 λΆν•œμ€ 경제적인 μ–΄λ €μ›€μœΌλ‘œ μΈν•œ μ‹λŸ‰ λΆ€μ‘±κ³Ό μ—λ„ˆμ§€ μžμ›μ˜ λΆ€μ‘±μœΌλ‘œ λ°œμƒν•˜μ˜€λ‹€. μ‹λŸ‰ 곡급을 μœ„ν•˜μ—¬ 산림은 밭으둜 κ°œκ°„λ˜μ—ˆκ³ , μ„νƒ„μ˜ λΆ€μ‘±μœΌλ‘œ μΈν•˜μ—¬ μ—λ„ˆμ§€μ›μœΌλ‘œ μ‚¬μš©ν•˜κΈ° μœ„ν•œ λ¬΄λΆ„λ³„ν•œ 벌λͺ©μ΄ μ§„ν–‰λ˜μ–΄ κ΄‘λ²”μœ„ν•¨ μ‚°λ¦Ό 황폐화가 κ°€μ†ν™”λ˜μ—ˆλ‹€. μ‚°λ¦Ό ν™©νν™”μ˜ λ¬Έμ œμ μ€ λΆν•œμ—μ„œλ„ μΈμ‹ν•˜μ—¬ κ΄€λ ¨ 정책을 μ§„ν–‰ν•˜λŠ” λ“±μ˜ λ…Έλ ₯을 ν•˜μ˜€μ§€λ§Œ, μ§€μ†λ˜λŠ” κ²½μ œλ‚œκ³Ό ν•œκ΅­κ³Όμ˜ 관계 μ•…ν™”λ‘œ μΈν•˜μ—¬ 효과적으둜 이루어지지 μ•Šκ³  μžˆλ‹€. λΆν•œμ˜ μ‚°λ¦Ό ν™©νν™”λŠ” λΆν•œλΏ μ•„λ‹ˆλΌ ν•œλ°˜λ„μ˜ ν™˜κ²½κ³Ό 동뢁아에 μ‚¬νšŒ 경제적으둜 영ν–₯을 μ£Όκ³  있기 λ•Œλ¬Έμ— 볡원이 μ‹œκΈ‰ν•œ 상황이며 μΆ”ν›„ ν•œκ΅­κ³Όμ˜ 관계가 κ°œμ„ λ˜μ—ˆμ„ λ•Œ 효과적인 볡원 사업 지원을 μœ„ν•΄μ„œλŠ” μ •ν™•ν•œ ν˜„ν™©κ³Ό 규λͺ¨λ₯Ό νŒŒμ•…ν•˜λŠ” 것이 μ€‘μš”ν•˜λ‹€. λΆν•œμ€ ν˜„μž¬ μ ‘κ·Ό λΆˆκ°€ μ§€μ—­μœΌλ‘œ ν˜„μž₯쑰사λ₯Ό ν†΅ν•œ ν˜„ν™© νŒŒμ•…μ΄ λΆˆκ°€λŠ₯ν•˜κΈ° λ•Œλ¬Έμ— μœ„μ„±μ˜μƒμ„ μ‚¬μš©ν•œ 원격탐사가 κ°€μž₯ 효과적인 방법이닀. λ˜ν•œ μ‚°λ¦Ό ν™©νν™”λŠ” 단기간에 λ‚˜νƒ€λ‚˜λŠ” ν˜„μƒμ΄ μ•„λ‹ˆλΌ μž₯기간에 걸쳐 μ§„ν–‰λ˜λŠ” ν˜„μƒμ΄κΈ° λ•Œλ¬Έμ— λ‹€μ€‘μ‹œκΈ°λ‘œ 뢄석할 ν•„μš”κ°€ μžˆλ‹€. λ”°λΌμ„œ λ³Έ μ—°κ΅¬μ—μ„œλŠ” λΆν•œμ˜ μ‚°λ¦Ό 황폐화가 μ‹¬ν™”λ˜κΈ° μ‹œμž‘ν•œ 1990λ…„λŒ€ 이후인 2000λ…„λΆ€ν„° κ°€μž₯ 졜근인 2020λ…„κΉŒμ§€ 20λ…„ λ™μ•ˆμ˜ λΆν•œ μ‚°λ¦Ό 황폐화 ν˜„ν™©μ„ νŒŒμ•…ν•˜λŠ” 것을 기본으둜 두 가지 연ꡬ 가섀을 μ„Έμ›Œ 리λ₯Ό ν™•μΈν•˜κ³ , 황폐화 진행이 μ–Όλ§ˆλ‚˜ λ˜μ—ˆλŠ”μ§€, λ³΅μ›μ‚¬μ—…μ˜ μ„±κ³Όκ°€ μžˆμ—ˆλŠ”μ§€ μ‚΄νŽ΄λ³΄κ³ μž ν•œλ‹€. 이λ₯Ό 톡해 μΆ”ν›„ 볡원 사업을 진행할 λ•Œ, 체계적인 κ³„νšμ„ μ„ΈμšΈ 수 μžˆλŠ” 기초자료둜 μ“Έ 수 μžˆλ„λ‘ ν•˜λŠ” 것이 연ꡬ λͺ©ν‘œμ΄λ‹€. 이λ₯Ό μœ„ν•˜μ—¬ 미ꡭ의 지리정보 ν”Œλž«νΌμΈ Google Earth Engine을 ν†΅ν•˜μ—¬ ν”½μ…€ 기반 감독 λΆ„λ₯˜ 랜덀 포레슀트(Random Forest) 방법을 μ‚¬μš©ν•˜μ—¬ 토지 피볡 λΆ„λ₯˜λ₯Ό μ§„ν–‰ν•˜κ³ , 이λ₯Ό 기반으둜 Change Detection(λ³€ν™” 감지)을 ν•˜μ—¬ μ–΄λŠ μ§€μ—­μ—μ„œ 황폐화가 μ§„ν–‰λ˜μ—ˆλŠ”μ§€, μ‚°λ¦Ό 면적이 μ–Όλ§ˆλ‚˜ λ³€ν™”ν•˜μ˜€λŠ”μ§€ μ‚΄νŽ΄λ³΄μ•˜λ‹€. 뢄석을 μ§„ν–‰ν•œ κ²°κ³Ό, 2000λ…„-2010λ…„ λ™μ•ˆ λΆν•œμ˜ μ‚°λ¦Ό λΉ„μœ¨μ€ 전체 면적의 μ•½ 72.5%μ—μ„œ μ•½ 61%둜 μ•½ 11.5% 정도 κ°μ†Œν•œ κ²ƒμœΌλ‘œ λ‚˜νƒ€λ‚¬λ‹€. 이와 λ°˜λ©΄μ— 농지와 λ‚˜μ§€μ˜ λΉ„μœ¨μ€ 각각 μ•½ 7%, μ•½ 2% μ¦κ°€ν•œ κ²ƒμœΌλ‘œ λ‚˜νƒ€λ‚˜ λ¬΄λΆ„λ³„ν•œ λ²Œμ±„μ™€ κ°œκ°„μœΌλ‘œ μΈν•œ μ‚°λ¦Ό 황폐화가 μ‹¬κ°ν•˜λ‹€λŠ” 것을 보여쀀닀. λ³€ν™”κ°€ κ°€μž₯ 많이 λ‚˜νƒ€λ‚œ 지역은 ν‰μ•ˆλ„, 함경도, 강원도 μ§€μ—­μœΌλ‘œ λ‚˜νƒ€λ‚¬μœΌλ©°, λ³€ν™”κ°€ κ°€μž₯ 적게 λ‚˜νƒ€λ‚œ 지역은 황해도 μ§€μ—­μœΌλ‘œ λ‚˜νƒ€λ‚¬λ‹€. 2010λ…„-2020λ…„ λ™μ•ˆμ˜ λΆν•œμ˜ μ‚°λ¦Ό λΉ„μœ¨μ€ μ•½ 61%μ—μ„œ μ•½ 62%둜 μ•½ 1%정도 μ¦κ°€ν•˜μ˜€μœΌλ©°, 농지도 μ•½ 3% μ¦κ°€ν•˜μ˜€λ‹€. 이와 λ°˜λ©΄μ— λ‚˜μ§€ λΉ„μœ¨μ€ μ•½ 4% κ°μ†Œν•˜μ—¬ 본격적인 μ‚°λ¦Ό 볡원 사업을 μ‹œμž‘ν•œ 2016λ…„ 이후 μ‚°λ¦Ό λΉ„μœ¨μ΄ μ•½κ°„ μƒμŠΉν•˜κ³  λ‚˜μ§€ λΉ„μœ¨μ΄ κ°μ†Œν•˜μ˜€μœΌλ‚˜ 농지 λΉ„μœ¨μ΄ μ¦κ°€ν•œ κ²ƒμœΌλ‘œ 보아 μ‚°λ¦Ό 볡원이 μ„±κ³΅μ μœΌλ‘œ 이루어지지 μ•Šμ•˜μœΌλ©°, λ¬΄λΆ„λ³„ν•œ κ°œκ°„ λ˜ν•œ μ§€μ†λ˜κ³  μžˆλ‹€λŠ” 것을 보여쀀닀. λ³€ν™”κ°€ κ°€μž₯ 크게 μΌμ–΄λ‚œ 지역은 황해도, 함경도 강원도 μ§€μ—­μœΌλ‘œ λ‚˜νƒ€λ‚¬μœΌλ©°, λ³€ν™”κ°€ κ°€μž₯ 적게 μΌμ–΄λ‚œ 지역은 ν‰μ•ˆλ„ μ§€μ—­μœΌλ‘œ λ‚˜νƒ€λ‚¬λ‹€. 20λ…„ λ™μ•ˆ κ³΅ν†΅μ μœΌλ‘œ λ³€ν™”κ°€ 많이 μΌμ–΄λ‚œ 지역은 함경도 κ°•μ›λ„λ‘œ, 뢄석결과λ₯Ό 톡해 이 μ§€μ—­μ—μ„œ κ°œκ°„κ³Ό λ²Œμ±„κ°€ 많이 μΌμ–΄λ‚¬μŒμ„ μ•Œ 수 μžˆλ‹€.Deforestation destroys forest ecosystems and reduces the functions of forests, such as reducing water storage and supply and air pollution. The degradation of forests due to deforestation harms climate change response and air quality. North Korea is one of the world's three deforested areas, and according to the research results of the National Institute of Forestry and Science, about 28% of the forest has been degraded from the 1990s until recently. However, as there are no official statistics, it is necessary to accurately identify the current situation for future restoration. Unlike general deforestation, North Korea was caused by a shortage of food and energy resources due to economic difficulties. Forests were cleared into fields for food supply, and extensive deforestation was accelerated by indiscriminate logging for use as an energy source due to a lack of coal. Although North Korea has recognized the problem of deforestation and implemented related policies, it has not been effectively implemented due to the continuing economic difficulties and deterioration of relations with South Korea. Since deforestation in North Korea has a socio-economic impact on North Korea and the environment on the Korean Peninsula and in Northeast Asia, restoration is urgently needed. In addition, it is important to know the exact current status and scale of deforestation for effective restoration project support when relations with Korea improve in the future. Since North Korea is currently inaccessible and it is impossible to determine the current situation through field surveys, remote sensing using satellite imagery is the most effective method. In addition, since deforestation is not a short-term phenomenon, but a long-term phenomenon, it is necessary to analyze it in multiple periods. Therefore, in this study, the status of deforestation in North Korea for 20 years from 2000 to 2020 after the 1990s, when deforestation in North Korea began to intensify, was identified, and two research hypotheses were established and confirmed. This study aims to enable it to be used as basic data for systematic planning when conducting a restoration project in the future. To this end, land cover classification is carried out using the pixel-based supervised classification random forest method through Google Earth Engine, a geographic information platform in the United States, and based on this, change detection is performed to determine the extent of devastation in an area. We looked at the progress and how much the forest area had changed. As a result of the analysis, the proportion of forests in North Korea decreased by about 11.5% from about 72.5% of the total area to about 61% from 2000 to 2010. On the other hand, the ratio of cropland and bareland increased by about 7% and about 2%, respectively, indicating that the deforestation caused by reckless logging and clearing is serious. The regions with the most changes were Pyeongan-do, Hamgyeong-do, and Gangwon-do, and the region with the least change was Hwanghae-do. During 2010-2020, the proportion of forests in North Korea increased by about 1% from about 61% to about 62%, and the cropland also increased by about 3%. When the full-scale forest restoration project began in North Korea, the ratio of bareland decreased by about 4% and the ratio of the forest increased slightly. Hwanghae-do and Gangwon-do, Hamgyeong-do showed the largest change, and Pyeongan-do show the least change. Gangwon-do, Hamgyeong-do, has seen many changes in common over the past 20 years, and the analysis results show that clearing and logging took place a lot in this area.Chapter 1. Introduction 2 1.1. Study Background and Purpose of Research 2 Chapter 2. Literature Review 5 2.1. Deforestation of North Korea 5 2.2. Random Forest using GEE 9 2.3. Change Detection 12 Chapter 3. Materials and Methods 14 3.1. Study Area and Materials 14 3.1.1. Study Area 14 3.1.2. Materials 15 3.2. Methods 21 3.2.1. Dataset and Pre-processing 21 3.2.2. Random Forest using GEE 22 3.2.3. Change Detection 23 Chapter 4. Results and Discussions 24 4.1. Results of Radom Forest 24 4.2. Results of Change Detection 28 4.2.1. 2000-2010 28 4.2.2. 2010-2020 30 4.2.3. 2000-2020 32 4.2.4. Regional Results 33 4.3. Discussions 46 Chapter 5. Conclusion 48 Bibliography 50 Abstract in Korean 55석

    Spatiotemporal approach for estimating potential CO2 sequestration by reforestation in the Korean Peninsula

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    A forest is one of the carbon sinks in the terrestrial ecosystem; it is a major target for securing CO2 sequestration to achieve carbon neutrality. Reforestation is a forest management method that could attain carbon fixation and forest degradation recovery at the same time, but quantitative research has not been actively conducted. The purpose of this study is to identify the target areas for reforestation through changes in land cover in the Korean Peninsula and to quantify the potential CO2 sequestration effect of reforestation. According to the land cover change through satellite imagery, the area of settlements in the Republic of Korea (ROK) was the most dominant (+3,371 km2), and the main change occurred from cropland to settlements. The forest area increased by +1,544 km2 from 68,264 km2 in the 1980s to 69,809 km2 in the late 2010s. The forest decreased by 7,526 km2, accounting for 5.68% of the entire land area of the Democratic People's Republic of Korea (DPRK), and cropland increased by 5,222 km2 which is 5.12%. Assuming that the target of reforestation is an area whose land cover was a forest in the past and then converted to cropland, wetland, or bare ground, the area of the target decreased as the reference period was applied more recently. As a result of comparing the late 2000s to the late 2010s, the ROK's annual net carbon sequestration due to reforestation is predicted to be 10,833,600 Mg CO2 yrβˆ’1 in 2050 and 20,919,200 Mg CO2 yrβˆ’1 in 2070. In the DPRK, 14,236,800 Mg CO2 yrβˆ’1 in 2050 and 27,490,400 Mg CO2 yrβˆ’1 in 2070 were predicted. Reforestation in the Korean Peninsula was analyzed to have sufficient potential to secure a carbon sink, and the DPRK in particular was analyzed to be able to play a role in overseas reforestation
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