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Mangroves are the true heroes of "blue carbon": they soak up huge amounts of CO₂, but measuring above‑ground carbon (AGC) is tricky. Dense canopies saturate satellite images, making it hard to tell how much biomass is actually there. To tackle this, researchers combined two technologies: drone‑mounted LiDAR (UAV) and data from several satellites (Sentinel‑1, Sentinel‑2, and ALOS PALSAR‑2). LiDAR provides canopy height (CH) with centimeter precision, while satellites deliver spectral and textural information over large areas.

In the Maowei Sea mangrove zone in China, the team extracted over fifty features (height, vegetation indices, radar texture) and fed them into a Random Forest model, fine‑tuned with Recursive Feature Elimination. The outcome? An R² of 0.75 and a root‑mean‑square error of 14.18 Mg C per hectare, far better than a satellite‑only model. CH turned out to be the most important predictor, overcoming spectral saturation in the densest stands.

The model estimated a total of 88,363.73 Mg of above‑ground carbon in the study area, averaging 53.01 Mg C per hectare. This shows that merging high‑resolution aerial data with satellite observations can produce more accurate, scalable carbon maps—crucial for monitoring coastal ecosystems under rapid climate change.

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LiDAR (Light Detection and Ranging) emits laser pulses toward the ground and records the return time to reconstruct a three‑dimensional vegetation structure. In mangrove forests, where canopies are intertwined and leaf cover is nearly continuous, aerial LiDAR can penetrate gaps and produce a canopy height (CH) map with sub‑meter resolution. This information is crucial because aboveground biomass (AGB) correlates almost linearly with the power of CH (often modeled as AGB = a·CH^b).

Complementary satellite data include: Sentinel‑1 (C‑band radar, sensitive to structure and moisture), Sentinel‑2 (multispectral, visible and NIR bands for NDVI, EVI, etc.), and ALOS PALSAR‑2 (L‑band, penetrates denser vegetation). Textural features (e.g., entropy, contrast) are derived from gray‑level co‑occurrence matrices (GLCM) and capture spatial variability of reflectance, useful for distinguishing high‑biomass areas from degraded zones.

The Random Forest model is an ensemble of decision trees that reduces overfitting through bootstrap aggregating (bagging). Recursive Feature Elimination (RFE) iteratively removes the least important variables, enhancing model parsimony and generalization. Variable importance is assessed via Gini impurity reduction or increase in prediction error when a feature is permuted.

In the Maowei Sea case, combining CH with spectral indices (NDVI, SAR backscatter) and textures overcame the spectral saturation typical of optical sensors in dense forests, yielding a more reliable AGC estimate. This approach is scalable: once calibrated, it can be applied to other coastal areas, reducing reliance on costly large‑scale LiDAR flights.

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Authors:
Xuzhi MaiQuan LiWeifeng XuSongwen DengWenhuan WangWenqian WuWei ZhangYinghui Wang
Date Published:
Original Article www.mdpi.com
Fact-check verified on 05/06/2026
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Creative Commons License CC BY-NC-SA 4.0

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