Project
Land + Carbon

Measuring Biomass in Smallholder Forest Restoration

Drone–satellite biomass modeling — Legal Amazon, Mato Grosso, Brazil
Year
2026
Location
Alta Floresta, Mato Grosso, Brazil
Context
Yale School of the Environment · Ambrecht Family Fellowship · with Instituto Centro de Vida (ICV)
Methods
Google Earth Engine, drone multispectral photogrammetry, random forest with spatial-block cross-validation, Python, GIS
Data
GEDI L4A, MapBiomas Collection 9, GLAD canopy height, Sentinel-2, drone CHM + NDVI
The Challenge

Landscape-scale restoration in the Amazon depends on thousands of smallholders, but the measurement that would let them enter carbon markets — or simply show that their plantings are working — is priced for industrial projects, not for a two-hectare plot.

The obvious shortcut, wall-to-wall satellite biomass products, fails here: calibrated on closed, high-biomass forest, they saturate over young regrowth. Across the secondary forest surrounding these plots, ESA CCI reads a near-constant ~175 Mg/ha where field-calibrated LiDAR reads about 60. A model trained to reproduce it inherits that blindness, and cannot tell a three-year-old planting from a twenty-year-old stand.

Approach

Instituto Centro de Vida (ICV) holds drone surveys across a cluster of restoration plots in north-central Mato Grosso. The work builds a biomass estimate from that drone structure alone, anchored to a reference that can actually resolve low biomass.

  • Reference — GEDI L4A spaceborne LiDAR, field-calibrated at the 25 m footprint, restricted to mapped secondary vegetation.
  • Purity filter — footprints less than 80% within secondary forest are dropped, removing edge contamination from pasture and mature forest.
  • Analogous envelope — the reference pool is widened across the state to secondary forest matching the study area's precipitation and elevation range, yielding 22,331 clean footprints.
  • Parsimonious predictors — four terms the drone can measure: mean and 90th-percentile canopy height, canopy roughness, and NDVI. A random forest is fit with spatial-block cross-validation so accuracy is not inflated by autocorrelation.
  • Application — each plot's drone structure is passed to the model directly; the height-source transfer is reported as uncertainty rather than silently calibrated away.
Key Findings
  • Twelve plots (3–4 years old) hold an estimated 4–51 Mg/ha, median ~24 — consistent with early regrowth, and far below what a saturating reference would have produced.
  • Error scales with stature, not age. In the plots' height regime the uncertainty is ~30 Mg/ha; stratified by age instead, it stays flat near 50, because a young age class contains a wide spread of structures.
  • Every plot falls within one standard deviation of same-age natural regeneration, and above its median. Young secondary-forest biomass is strongly right-skewed, so median and mean point in opposite directions; both are reported.
  • The residual scatter is genuine structure-to-biomass uncertainty, not noise in the reference. Local allometry is the single change that would tighten it most.
Why It Matters

Restoration finance depends on measurement that distributed smallholders can actually afford. Anchoring a drone-scale model to spaceborne LiDAR rather than to a saturating raster makes screening and benchmarking possible without a field campaign, and states the accuracy honestly enough to know where a field campaign is still required. The pipeline is packaged to retarget to another region by editing a config file, not the code.

Supporting Figures
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