Abstract

Savanna ecosystems are challenging to map and monitor as their vegetation is highly dynamic in space and time. Understanding the structural diversity and biomass distribution of savanna vegetation requires high-resolution measurements over large areas and at regular time intervals. These requirements cannot currently be met through field-based inventories nor spaceborne satellite remote sensing alone. UAV-based remote sensing offers potential as an intermediate scaling tool, providing acquisition flexibility and cost-effectiveness. Yet despite the increased availability of lightweight LiDAR payloads, the suitability of UAV-based LiDAR for mapping and monitoring savanna 3D vegetation structure is not well established. We mapped a 1 ha savanna plot with terrestrial-, mobile- and UAV-based laser scanning (TLS, MLS, and ULS), in conjunction with a traditional field-based inventory (n = 572 stems > 0.03 m). We treated the TLS dataset as the gold standard against which we evaluated the degree of complementarity and divergence of structural metrics from MLS and ULS. Sensitivity analysis showed that MLS and ULS canopy height models (CHMs) did not differ significantly from TLS-derived models at spatial resolutions greater than 2 m and 4 m respectively. Statistical comparison of the resulting point clouds showed minor over- and under-estimation of woody canopy cover by MLS and ULS, respectively. Individual stem locations and DBH measurements from the field inventory were well replicated by the TLS survey (R2 = 0.89, RMSE = 0.024 m), which estimated above-ground woody biomass to be 7% greater than field-inventory estimates (44.21 Mg ha−1 vs 41.08 Mg ha−1). Stem DBH could not be reliably estimated directly from the MLS or ULS, nor indirectly through allometric scaling with crown attributes (R2 = 0.36, RMSE = 0.075 m). MLS and ULS show strong potential for providing rapid and larger area capture of savanna vegetation structure at resolutions suitable for many ecological investigations; however, our results underscore the necessity of nesting TLS sampling within these surveys to quantify uncertainty. Complementing large area MLS and ULS surveys with TLS sampling will expand our options for the calibration and validation of multiple spaceborne LiDAR, SAR, and optical missions.

Highlights

  • This article is an open access articleSavanna vegetation structure is shaped by the interaction of climate, soils and a variety of disturbance agents acting at multiple spatio-temporal scales [1,2]

  • Sensitivity analysis showed that these differences remained significant until a canopy height models (CHMs) resolution of 2 m was reached for the Terrestrial laser scanning (TLS)-mobile laser scanning (MLS) comparisons, and 4 m for TLS-UAV-based laser scanning (ULS) and MLS-ULS comparisons (KS-test, p > 0.05)

  • Were negligible for most applications, but there was a large difference in the acquisition time, with MLS and ULS offering distinct advantages

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Summary

Introduction

This article is an open access articleSavanna vegetation structure is shaped by the interaction of climate, soils and a variety of disturbance agents acting at multiple spatio-temporal scales [1,2]. The actions of fire, herbivores, termites, and cyclones have marked effects on the structure of savanna tree crowns, leading to high degree of structural diversity [3,4,5]. 2021, 13, 257 heterogeneous spatial patterning, and because of disturbance driven variability in individual tree crown structure [6]. Structural attributes such as height, canopy diameter, and projected foliage cover are commonly assessed through field inventories—but these measures are often subjective and prone to sampling errors [7]. Robust assessment of structural change in tropical savannas requires methods that can account for spatial and temporal heterogeneity, and a high level of accuracy and precision in structural attribute measurement

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