Abstract

A key aspect of vegetation monitoring from LiDAR is concerned with the use of comparable data acquired from multitemporal surveys and from different sensors. Accurate digital elevation models (DEMs) to derive vegetation products, are required to make comparisons among repeated LiDAR data. Here, we aimed to apply an improved empirical method based on DEMs of difference, that adjust the ground elevation of a low-density LiDAR dataset to that of a high-density LiDAR one for ensuring credible vegetation changes. The study areas are a collection of six sites over the Sierra de Gredos in Central Spain. The methodology consisted of producing “the best DEM of difference” between low- and high-density LiDAR data (using the classification filter, the interpolation method and the spatial resolution with the lowest vertical error) to generate a local “pseudo-geoid” (i.e., continuous surfaces of elevation differences) that was used to correct raw low-density LiDAR ground points. The vertical error of DEMs was estimated by the 50th percentile (P50), the normalized median absolute deviation (NMAD) and the root mean square error (RMSE) of elevation differences. In addition, we analyzed the effects of site-properties (elevation, slope, vegetation height and distance to the nearest geoid point) on DEMs accuracy. Finally, we assessed if vegetation height changes were related to the ground elevation differences between low- and high-density LiDAR datasets. Before correction and aggregating by sites, the vertical error of DEMs ranged from 0.02 to −2.09 m (P50), from 0.39 to 0.85 m (NMDA) and from 0.54 to 2.5 m (RMSE). The segmented-based filter algorithm (CSF) showed the highest error, but there were not significant differences among interpolation methods or spatial resolutions. After correction and aggregating by sites, the vertical error of DEMs dropped significantly: from −0.004 to −0.016 m (P50), from 0.10 to 0.06 m (NMDA) and from 0.28 to 0.46 m (RMSE); and the CSF filter algorithm continued showing the greatest vertical error. The terrain slope and the distance to the nearest geoid point were the most important variables for explaining vertical accuracy. After corrections, changes in vegetation height were decoupled from vertical errors of DEMs. This work showed that using continuous surfaces with the lowest elevation differences (i.e., the best DEM of difference) the raw elevation of low-density LiDAR was better adjusted to that of a benchmark for being adapted to site-specific conditions. This method improved the vertical accuracy of low-density LiDAR elevation data, minimizing the random nature of vertical errors and decoupling vegetation changes from those errors.

Highlights

  • A detailed understanding of the magnitude and source of error in LiDAR elevation data and its derived products (i.e., digital elevation models (DEMs) and canopy height models [CHMs]) is necessary for operational use of LiDAR in deriving accurate forest inventory metrics [1,2,3,4]

  • This approach will allow capturing of the micro-topography of each site and will reduce random or methodological errors that would be very difficult to correct by using only checkpoints. To accomplish this main objective: (i) we explored the effects of methodological factors on vertical errors of DEMs carrying out a factorial ANOVA; (ii) we assessed how site-properties explained the observed vertical errors of DEMs by running generalized additive models (GAMs) using a random sampling, (iii) we recalculated the DEMs and the canopy height models (CHMs) from the corrected low-density LiDAR data using the best method; and (iv) we assessed if vegetation height changes continued or not related to DEMs elevation errors

  • Standardization of ground elevation is obligatory for comparison of LiDAR derived comparison of vegetation height changes from low- and high-density LiDAR datasets, forest metrics at different dates

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Summary

Introduction

A detailed understanding of the magnitude and source of error in LiDAR elevation data and its derived products (i.e., digital elevation models (DEMs) and canopy height models [CHMs]) is necessary for operational use of LiDAR in deriving accurate forest inventory metrics [1,2,3,4]. When true ground points are not available, interpolated checkpoints from high-density LiDAR ground data have been used as benchmark DEM to either assess the quality, correct other less accurate DEMs, or both, as photogrammetric [9,11] or satellite derived ones (i.e., SRTM) [12,13] using DEMs of difference as procedure. This method has demonstrated being robust to estimate vertical errors but only a few times, it has been used to correct raw elevation values [12,13]. Elevation differences were corrected by means of regression analysis, using several checkpoints but the corrected

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