基于ALOS PALSAR-Sentinel - landsat 8传感器协同模型的地中海松林生物量时间变化

Remote. Sens. Pub Date : 2023-07-06 DOI:10.3390/rs15133430
Edward A. Velasco Pereira, María A. Varo Martínez, F. Gómez, R. Navarro-Cerrillo
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引用次数: 1

摘要

目前,气候变化需要对森林生物量中储存的碳进行量化。合成孔径雷达(SAR)数据在提供生态系统结构和生物量相关信息方面比其他遥感探测测量方法具有显著优势。利用ALOS-PALSAR、Sentinel 1和Landsat 8数据,建立非参数随机森林回归模型,评估地中海松林地上生物量(AGB)、基底面积(G)和树密度(N)的变化。从随机森林模型中选择的变量与NDVI和光学纹理变量相关。2015年生物量模型中,综合ALS-ALOS2-Sentinel 1-Landsat 8数据(R2 = 0.59)和ALOS2-Sentinel 1-Landsat 8数据(R2 = 0.50)的生物量模型表现最好。验证集显示,R2值在0.55 (ALOS2-Sentinel 1- landsat 8模型)至0.60 (ALS-ALOS2-Sentinel 1- landsat 8模型)之间变化,RMSE低于20 Mg ha−1。值得注意的是,个体Sentinel 1 (R2 = 0.49)。和Landsat 8 (R2 = 0.47)模型得出了相同的结果。2020年,AGB模型ALOS2-Sentinel 1- landsat 8的性能R2 = 0.55(验证R2 = 0.70), RMSE为9.93 Mg ha−1。对于2015年的森林结构变量,包括ALOS PAL-SAR 2-Sentinel 1 Landsat 8在内的随机森林模型解释了总方差的30%到55%,对于2020年的模型,它们解释了25%到55%。利用ALOS PALSAR 2-Sentinel 1-Landsat 8模型生成了2015年和2020年森林结构变量图,以评估这一时期的变化。地上生物量(AGB)图、胸径(dbh)图和优势高度(Ho)图在整个研究区内具有一致性。然而,随机森林模型低估了较高的生物量水平(100 Mg ha - 1),高估了中等生物量水平(30-45 Mg ha - 1)。AGB变化图显示,在研究期间,AGB的值从增加43.3 Mg ha - 1到减少- 68.8 Mg ha - 1不等。开放获取卫星光学和SAR数据的整合可以显著提高AGB估算值,从而实现对森林碳动态的持续和长期监测。
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Temporal Changes in Mediterranean Pine Forest Biomass Using Synergy Models of ALOS PALSAR-Sentinel 1-Landsat 8 Sensors
Currently, climate change requires the quantification of carbon stored in forest biomass. Synthetic aperture radar (SAR) data offers a significant advantage over other remote detection measurement methods in providing structural and biomass-related information about ecosystems. This study aimed to develop non-parametric Random Forest regression models to assess the changes in the aboveground forest biomass (AGB), basal area (G), and tree density (N) of Mediterranean pine forests by integrating ALOS-PALSAR, Sentinel 1, and Landsat 8 data. Variables selected from the Random Forest models were related to NDVI and optical textural variables. For 2015, the biomass models with the highest performance integrated ALS-ALOS2-Sentinel 1-Landsat 8 data (R2 = 0.59) by following the model using ALS data (R2 = 0.56), and ALOS2-Sentinel 1-Landsat 8 (R2 = 0.50). The validation set showed that R2 values vary from 0.55 (ALOS2-Sentinel 1-Landsat 8) to 0.60 (ALS-ALOS2-Sentinel 1-Landsat 8 model) with RMSE below 20 Mg ha−1. It is noteworthy that the individual Sentinel 1 (R2 = 0.49). and Landsat 8 (R2 = 0.47) models yielded equivalent results. For 2020, the AGB model ALOS2-Sentinel 1-Landsat 8 had a performance of R2 = 0.55 (validation R2 = 0.70) and a RMSE of 9.93 Mg ha−1. For the 2015 forest structural variables, Random Forest models, including ALOS PAL-SAR 2-Sentinel 1 Landsat 8 explained between 30% and 55% of the total variance, and for the 2020 models, they explained between 25% and 55%. Maps of the forests’ structural variables were generated for 2015 and 2020 to assess the changes during this period using the ALOS PALSAR 2-Sentinel 1-Landsat 8 model. Aboveground biomass (AGB), diameter at breast height (dbh), and dominant height (Ho) maps were consistent throughout the entire study area. However, the Random Forest models underestimated higher biomass levels (>100 Mg ha−1) and overestimated moderate biomass levels (30–45 Mg ha−1). The AGB change map showed values ranging from gains of 43.3 Mg ha−1 to losses of −68.8 Mg ha−1 during the study period. The integration of open-access satellite optical and SAR data can significantly enhance AGB estimates to achieve consistent and long-term monitoring of forest carbon dynamics.
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